Atlantic Highly Migratory Species; Shortfin Mako Shark Management Measures; Final Amendment 11, 5358-5377 [2019-02946]
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Classification
There is good cause to waive prior
notice and an opportunity for public
comment on this action pursuant to 5
U.S.C. 553(b)(B). Providing an
opportunity for prior notice and
comment would be contrary to the
public interest because the SEZ closure
has been triggered by a second observed
M&SI, and immediate closure of the SEZ
is necessary to prevent additional
mortalities or serious injuries, which
may have unsustainable impacts on the
Hawaii pelagic stock of the false killer
whale. Furthermore, prior notice and
comment is unnecessary because the
take reduction plan final rule (77 FR
71259, November 29, 2012) that
implements the procedure for closing
the SEZ (codified at 50 CFR 229.37(d)(2)
and (e)) has already been subject to an
extensive public process, including the
opportunity for prior notice and
comment. All that remains is to notify
the public of the second observed
mortality and serious injury of a pelagic
false killer whale resulting from
commercial longline operations, and the
longline closure of the SEZ. Although
this action is being implemented
without the opportunity for prior notice
and comment, NMFS is soliciting and
will respond to public comments from
those affected by or otherwise interested
in this rule.
The NOAA Assistant Administrator
for Fisheries also finds good cause to
waive the 30-day delay in the
effectiveness of this action under 5
U.S.C. 553(d)(3). Failing to waive the
30-day delay in effectiveness would
likely result in additional interactions
and possible M&SI to the Hawaii pelagic
false killer whale stock. Under the
MMPA, NMFS must reduce M&SI of
marine mammal stocks protected by
take reduction plan regulations. This
includes taking action to close the SEZ
immediately upon a second observed
M&SI resulting from commercial
longlining in the EEZ. Accordingly, the
SEZ closure must be implemented
immediately to ensure compliance with
the provisions of the MMPA and the
take reduction plan regulations.
Nevertheless, NMFS recognizes the
need for fishermen to have time to haul
their gear and relocate to areas outside
of the SEZ; thus, NMFS makes this
action effective 7 days after filing this
document in the Federal Register.
This action is required by 50 CFR
229.37(e)(3), and is exempt from review
under Executive Order 12866.
Authority: 16 U.S.C. 1361 et seq.
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Dated: February 15, 2019.
Chris Oliver,
Assistant Administrator for Fisheries,
National Marine Fisheries Service.
[FR Doc. 2019–02995 Filed 2–15–19; 4:15 pm]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
relevant to this rule are available from
the HMS Management Division website
at https://www.fisheries.noaa.gov/topic/
atlantic-highly-migratory-species.
´
FOR FURTHER INFORMATION CONTACT: Guy
DuBeck or Karyl Brewster-Geisz at (301)
427–8503.
SUPPLEMENTARY INFORMATION:
Background
National Oceanic and Atmospheric
Administration
50 CFR Part 635
[Docket No. 180212159–9102–02]
RIN 0648–BH75
Atlantic Highly Migratory Species;
Shortfin Mako Shark Management
Measures; Final Amendment 11
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
NMFS is amending the 2006
Consolidated Atlantic Highly Migratory
Species (HMS) Fishery Management
Plan (FMP) based on the results of the
2017 stock assessment and a subsequent
binding recommendation by the
International Commission for the
Conservation of Atlantic Tunas (ICCAT)
for North Atlantic shortfin mako sharks.
The North Atlantic shortfin mako shark
stock is overfished and is experiencing
overfishing. Consistent with the
Magnuson-Stevens Fishery
Conservation and Management Act
(Magnuson-Stevens Act) and the
Atlantic Tunas Convention Act (ATCA),
NMFS is implementing management
measures that will reduce fishing
mortality on shortfin mako sharks and
establish the foundation for rebuilding
the shortfin mako shark population
consistent with legal requirements. The
final measures could affect U.S.
commercial and recreational fishermen
who target and harvest shortfin mako
sharks in the Atlantic Ocean, including
the Gulf of Mexico and Caribbean Sea,
by increasing live releases and reducing
landings. NMFS is also clarifying the
definition of fork length (FL) in the
definitions section of the HMS
regulations.
DATES: This final rule is effective on
March 3, 2019.
ADDRESSES: Copies of the Final
Amendment 11 to the 2006
Consolidated HMS FMP, including the
Final Environmental Impact Statement
(FEIS) containing a list of references
used in this document, the dusky shark
stock assessments, and other documents
SUMMARY:
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The North Atlantic shortfin mako
stock is managed primarily under the
authority of the Magnuson-Stevens Act
and also under ATCA. The 2006
Consolidated HMS FMP and its
amendments are implemented by
regulations at 50 CFR part 635. A brief
summary of the background of this final
rule is provided below. Additional
information regarding Atlantic shark
management can be found in the FEIS
accompanying this final rule for
Amendment 11, the 2006 Consolidated
HMS FMP and its amendments, the
annual HMS Stock Assessment and
Fishery Evaluation (SAFE) Reports, and
online at https://www.fisheries.
noaa.gov/topic/atlantic-highlymigratory-species.
The North Atlantic shortfin mako
shark (Isurus oxyrinchus) is a highly
migratory species that ranges across the
entire North Atlantic Ocean and is
caught by numerous countries. The
stock is predominantly caught offshore
in association with fisheries that
primarily target tunas and tuna-like
species. While these sharks are a valued
component of U.S. recreational and
commercial fisheries, U.S. catch
represents only approximately 9 percent
of the species’ total catch in the North
Atlantic by all reporting countries.
International measures are, therefore,
critical to the species’ effective
conservation and management.
Based on a 2017 ICCAT assessment,
on December 13, 2017, NMFS issued a
status determination finding the stock to
be overfished and experiencing
overfishing, applying domestic criteria.
The 2017 assessment estimated that
total North Atlantic shortfin mako
catches across all ICCAT parties are
currently between 3,600 and 4,750
metric tons (mt) per year. The
assessment further indicated that such
total catches would have to be at or
below 1,000 mt (72–79 percent
reductions) to prevent further
population declines, and total catches of
500 mt or less would be expected to
stop overfishing and begin rebuilding
the stock.
Based on this information and given
that the stock is primarily caught in
association with ICCAT fisheries,
ICCAT at its November 2017 meeting
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adopted management measures for
Atlantic shortfin mako in
Recommendation 17–08. The measures
largely focused on maximizing live
releases of Atlantic shortfin mako
sharks, allowing retention only in
certain limited circumstances,
increasing minimum size limits for
retention, and improving data collection
in ICCAT fisheries. ICCAT stated that
the measures in the Recommendation
were ‘‘expected to prevent the
population from decreasing further, stop
overfishing and begin to rebuild the
stock.’’
On March 2, 2018, NMFS
implemented an interim final rule using
emergency authority under the
Magnuson-Stevens Act, 16 U.S.C.
1855(c), to quickly implement measures
in the HMS recreational and commercial
fisheries consistent with
Recommendation 17–08. The emergency
measures were initially effective for 180
days, and on August 22, 2018, they were
extended to March 3, 2019 (83 FR
42452). This final rule is intended to
replace these emergency measures with
long-term measures.
A Notice of Intent (NOI) to prepare an
EIS for Amendment 11 of the
Consolidated HMS FMP was published
in the Federal Register on March 5,
2018 (83 FR 9255) and provided notice
of the availability of an Issues and
Options document for scoping. Based on
the alternatives presented and
commented on during scoping, NMFS
published a proposed rule for Draft
Amendment 11 on July 27, 2018 (83 FR
35590), and the Environmental
Protection Agency (EPA) published the
notice of availability of the Draft
Environmental Impact Statement (DEIS)
on July 27, 2018 (83 FR 35637). The
details of this rulemaking can be found
in the proposed rule and are not
repeated here.
During the comment period on the
proposed rule and DEIS, which lasted
for 73 days, NMFS conducted six public
hearings (Texas, Florida, North
Carolina, New Jersey, and
Massachusetts) and a public webinar. In
addition, NMFS presented Draft
Amendment 11 to the Atlantic HMS
Advisory Panel, four Atlantic Regional
Fishery Management Councils (the New
England, Mid-Atlantic, South Atlantic,
and the Gulf of Mexico Fishery
Management Councils), and the Atlantic
States Marine Fisheries Commission.
The comment period ended on October
8, 2018. The comments received on
Draft Amendment 11 and its proposed
rule, and responses to those comments,
are summarized below in the section
labeled ‘‘Response to Comments.’’
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This final rule implements the
measures preferred and analyzed in the
FEIS for Amendment 11 to the 2006
Consolidated HMS FMP in order to
address and establish a foundation for
rebuilding the North Atlantic shortfin
mako shark stock, which ICCAT will
adopt in 2019 after obtaining additional
scientific information, as set out in
Recommendation 17–08. It also includes
a clarification to the regulatory
definition of ‘‘FL (fork length),’’ as
proposed and discussed in the DEIS and
FEIS. The FEIS analyzed the direct,
indirect, and cumulative impacts on the
human environment as a result of the
preferred management measures. The
FEIS, including the preferred
management measures, was made
available on December 21, 2018 (83 FR
65670). On February 15, 2019, the
Assistant Administrator for NOAA
signed a Record of Decision (ROD)
adopting these measures as Final
Amendment 11 to the 2006
Consolidated HMS FMP. A copy of the
FEIS, including Final Amendment 11 to
the 2006 Consolidated HMS FMP, is
available from the HMS Management
Division (see ADDRESSES). In the FEIS,
NMFS divided the alternatives into the
following four broad categories for
organizational clarity and to facilitate
effective review: Commercial fishery,
recreational fishery, monitoring, and
rebuilding. NMFS fully considered 29
alternatives within these categories and
is implementing five measures, one in
the commercial fishery, two in the
recreational fishery (each regarding a
different regulation type), one regarding
monitoring, and one regarding
rebuilding the stock, to meet the
objectives of the rule and achieve at
least a 75 percent reduction in U.S.
shortfin mako shark landings consistent
with the suggested level of reduction
recommended in the stock assessment.
The stock assessment recommends this
level of reduction throughout the stock’s
range, and all ICCAT parties fishing on
the stock are committed to take the
specified measures to achieve the
needed reductions. NMFS’ detailed
analyses of the alternatives are provided
in the FEIS for Draft Amendment 11 (see
ADDRESSES for how to get a copy of the
FEIS) and a summary is provided in the
FRFA below.
In developing the final measures,
NMFS considered the commercial
retention restrictions and the 83-inch FL
recreational minimum size limit
temporarily put in place through the
emergency interim final rule, public
comments received on that rule, other
conservation and management measures
that have been implemented in the HMS
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fisheries since 2008 that have affected
shark fisheries or shark bycatch in other
fisheries, and public comments received
on the proposed rule and DEIS,
including comments provided at the
September 2018 HMS Advisory Panel
meeting. In response to public comment
on the proposed rule and the DEIS,
NMFS made three changes from the
proposed rule in the final rule. The first
change adopts a new commercial
measure that is a modified version of
the previously preferred measure. A
second change adopts a different
recreational size limit measure that was
not preferred in the proposed rule. A
third change clarifies the application of
retention restrictions for the few permit
holders who hold a commercial shark
permit and a permit that also allows
recreational landings of sharks. All
other proposed conservation measures,
as well as the proposed clarification of
the definition of ‘‘fork length,’’ did not
change between the proposed and final
rules. Measures that are different from
the proposed rule, or measures that
were proposed but not implemented, are
described in detail in the section titles,
‘‘Changes from the Proposed Rule.’’
Response to Comments
NMFS received a total of 30
individual written comments on the
proposed rule from fishermen, dealers,
and other interested parties along with
State of North Carolina, Commonwealth
of Massachusetts, the Mid-Atlantic and
New England Fishery Management
Councils, several shark conservation or
other environmental groups, including
Oceana, and several commercial and
recreational groups. Oral comments
were received from the South Atlantic
Fishery Management Council. All
written comments can be found at
https://www.regulations.gov/ by
searching for RIN 0648–BH75. All of the
comments received are summarized
below.
Comment 1: NMFS received multiple
comments expressing support for
Amendment 11 management measures
as well as comments opposing
implementation of ICCAT shortfin mako
shark recommendations. Commenters in
support of Amendment 11 wanted
management measures to prevent
overfishing of shortfin mako sharks by
placing limits and restrictions on fishing
that results in mortality of shortfin mako
sharks. They also stressed the need for
international cooperation if shortfin
mako shark measures are to be effective
and the need for all countries fishing on
the stock to implement comparable
regulations as required by ICCAT. In
addition, some commenters cited the
importance of shortfin mako sharks to
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the health of ocean ecosystems. One
commenter opposed any management
measures for shortfin mako sharks,
citing their understanding of previous
ICCAT stock assessment issues,
including the underlying uncertainties
with other shark stock assessments such
as the porbeagle shark assessment.
Specifically, this commenter stated that
ICCAT had recommended similar
regulations for porbeagle sharks after a
stock assessment, and later changed the
results after the United States supplied
additional information.
Response: NMFS agrees that shortfin
mako sharks play an important role in
maintaining ocean ecosystems, and
notes that there are statutory obligations
to effectively manage shark fisheries,
prevent overfishing, and achieve longterm sustainability of the stock. NMFS
has determined that the management
measures in this rule will address
overfishing and begin the process of
rebuilding the North Atlantic shortfin
mako shark stock as required by law,
understanding that any effective
rebuilding plan or measures to end
overfishing depend on effective
international measures, given that the
United States contributes to only a
portion of the fishing mortality on the
stock.
NMFS believes that the 2017 ICCAT
stock assessment for shortfin mako
sharks is not appropriately compared to
the previous stock assessment for
porbeagle sharks and generally does not
agree with the commenter’s implication
that the ICCAT assessments are
routinely flawed. The 2017 ICCAT stock
assessment for shortfin mako sharks
included many improvements in the
data and modeling compared to
previous shark stock assessments,
including past porbeagle and shortfin
mako shark assessments. NMFS has
determined that the 2017 SCRS shortfin
mako shark stock assessment is the best
scientific information available for
shortfin mako sharks, and NMFS is
using the results, as appropriate, as
required under National Standard 2 of
the Magnuson-Stevens Act.
Comment 2: NMFS received
comments about the stock assessment
methodology and results. A commenter
had concerns that the methodology
applied in evaluating the results of
different stock assessment models used
in the 2017 shortfin mako stock
assessment introduced an inappropriate
negative bias in the overall assessment
results. Other commenters were
concerned about the large change in
stock status between all the most recent
previous ICCAT stock assessment
results, the conversion rates used to
convert dressed weight to whole weight
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of sharks, the potential for underreporting of harvest by other ICCAT
members particularly those countries
that have larger fishing fleets than the
United States, and the potential
implications of the Marine Recreational
Information Program (MRIP) catch
estimates. These commenters requested
that NMFS postpone implementing
Amendment 11 until the next shortfin
mako shark stock assessment is
completed.
Response: While there is always
uncertainty in stock assessment data
inputs, model outputs, and the
subsequent interpretation of results, the
SCRS methodologies appropriately
considered how to best address such
uncertainties in this particular context.
The SCRS described these sources of
uncertainty and concluded that the 2017
stock assessment was an improvement
over previous assessments for shortfin
mako sharks, and reflects the best
scientific information available on the
status of the stock. ICCAT reviewed and
accepted the results for use in
management, and made specific
recommendations which the United
States is obligated to implement as
necessary and appropriate under ATCA.
NMFS is also required to take action to
end overfishing and rebuild the stock
under the Magnuson-Stevens Act given
the stock’s status as overfished with
overfishing occurring. If future stock
assessments reach different conclusions
regarding shortfin mako shark stock
status, and changes to management
measures are recommended by ICCAT,
or if NMFS determines that different
measures are needed to address
management of the stock, then such
changes may be considered at that time.
Regarding the comment expressing
concern that the United States used
incorrect conversion rates for dressed
weight to whole weight of sharks, this
issue has also come up in the context of
reporting to ICCAT. As discussed with
the ICCAT Advisory Committee at its
Fall meeting, the United States surveyed
other countries regarding the conversion
rates and the manner in which those
countries dress their sharks and then
reviewed the data it submitted to
ICCAT. Based on this review of the data
and the survey of other countries’
conversion factors, the United States
found errors in the shortfin mako shark
commercial landings data previously
submitted to ICCAT and determined
that changing the conversion rate to
match that used by Spain and Canada
was appropriate. Accordingly, the
United States submitted revised
estimates to ICCAT of U.S. harvest for
all years. NMFS has accordingly
updated all the numbers from the DEIS
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in the FEIS to reflect the updated
analyses, since the numbers in the DEIS
were based on the ICCAT submissions.
As a result of these revised estimates,
the U.S. proportion of shortfin mako
catches compared to all catches by all
countries was reduced from 11 percent
to 9 percent. For U.S. harvest, these
changes also resulted in a recalculation
of the relative contribution of
commercial and recreational fisheries to
domestic shortfin mako shark mortality.
The proportion of recreational to
commercial harvest is not equally split
with recreational harvest accounting for
58 percent and commercial harvest
(including landings and dead discards)
accounting for 42 percent.
Comment 3: NMFS received
comments regarding the timing and
process of this rulemaking. Commenters
urged NMFS to implement management
measures immediately based on the best
available science to rebuild the stock
and end overfishing. Other commenters
are concerned that this rulemaking is
premature since ICCAT could make
changes in upcoming meetings. Some
commenters felt the United States
should not act unilaterally, and
implement a rebuilding plan without
ICCAT. Another commenter stated that
NMFS has two years to implement
rebuilding plans and management
measures once the stock is determined
to be overfished and requested that
NMFS wait to implement Amendment
11.
Response: Amendment 11 is
responsive to ICCAT Recommendation
17–08, which is a binding
recommendation under the ICCAT
Convention, and the United States is
obligated to implement it through
regulations as necessary and appropriate
under ATCA. Due to the requirements
in Recommendation 17–08 and the
status of shortfin mako sharks, NMFS
worked to immediately implement the
requirements in Recommendation 17–08
via an emergency interim final rule (83
FR 8946; March 2, 2018). Under sections
305(c) and 304(e)(6) of the MagnusonStevens Act, NMFS has the authority to
implement interim measures to reduce
overfishing on an emergency basis for
180 days. Those measures can be
extended again for another 186 days if
necessary. NMFS later extended the
emergency rule for another 186 days;
these emergency measures expire on
March 3, 2019 (83 FR 42452; August 22,
2018). NMFS aims to have the
management measures in Amendment
11 in place by the time the emergency
rule expires or soon thereafter. If ICCAT
changes the measures in
Recommendation 17–08 at future
meetings, then the United States will be
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responsive to those changes, consistent
with ATCA and the Magnuson-Stevens
Act. NMFS does not have discretion to
delay implementation of management
measures adopted at ICCAT simply
because we anticipate there may be
additional or different ICCAT
recommendations in the future. This
action does not implement a unilateral
rebuilding plan in U.S. waters for
shortfin mako sharks. This action
establishes the foundation for an
international, ICCAT-recommended
rebuilding plan, understanding that
ICCAT intends to adopt such a plan in
the future and that the United States
will advocate for its development at that
forum.
Regarding the comment on the twoyear timeframe to implement
management measures being a reason to
delay implementation, we note that we
have an obligation to implement the
measures under ATCA and the ICCAT
treaty, and that the Magnuson-Stevens
Act requires NMFS to take measures to
end overfishing and to rebuild the
stocks. The regulatory process to amend
the 2006 Consolidated HMS FMP is a
lengthy process involving significant
public input and review; the two-year
reference in the Magnuson-Stevens Act
is not to be read as a delay in starting
that process, which could prevent
measures from being timely
implemented. Section 304(e)(6) allows
for interim measures to reduce
overfishing to be put in place until a
FMP amendment can be finalized; this
section of the Magnuson-Stevens Act
only allows for these interim measures
to be put in place pursuant to section
305(c), which limits the amount of time
emergency measures can be effective to
366 days. Based on these regulations,
NMFS published the emergency interim
final rule per the authority in sections
305(c) and 304(e)(6) of the MagnusonStevens Act, and is implementing longterm management measures to address
overfishing and establish a foundation
for rebuilding shortfin mako sharks with
Amendment 11, consistent with the
Magnuson-Stevens Act.
Comment 4: NMFS received
comments in support of adding a sunset
clause to this rulemaking, which would
remove regulations implemented by
Amendment 11 if ICCAT makes changes
to Recommendation 17–08.
Response: A ‘‘sunset clause’’ on
regulations to address overfishing of
shortfin mako sharks would not be
consistent with the ICCAT
recommendation, or the need to rebuild
the stock, which could take decades
based on the 2017 stock assessment. If
ICCAT recommends changes to
management measures in the future,
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NMFS would implement necessary and
appropriate responsive regulatory
changes at that time, consistent with
applicable laws.
Comment 5: NMFS received
comments regarding the implementation
of the ICCAT regulations and fishing
operations by other countries. The
commenters had concerns that other
countries are not implementing the
Recommendation and about the pace of
the U.S. implementation when
compared to other countries.
Commenters also wondered if other
ICCAT countries have electronic
monitoring systems or observers for
their fleets. In addition, the commenters
believe that U.S. fishermen will be held
accountable for an excessive share of the
conservation burden in future ICCAT
management measures.
Response: NMFS acknowledges that
countries other than the United States
are responsible for the majority of North
Atlantic shortfin mako shark fishing
mortality, hence the need for
international coordination through
ICCAT on measures to end overfishing
and rebuild the stock. Regardless of
other countries’ capability to adequately
implement and enforce ICCAT
recommendations, the United States
remains obligated under ATCA to
implement ICCAT recommendations. As
a responsible party to ICCAT, NMFS
will continue to work collaboratively
within the ICCAT process and advocate
for an effective international rebuilding
plan, emphasizing the need for all
parties to address their relative share of
contributions to fishing mortality and
for equitable management measures.
Comment 6: NMFS should implement
an EFH designation for shortfin mako
sharks.
Response: NMFS has recently
updated EFH designations for shortfin
mako sharks under Amendment 10 to
the 2006 Consolidated HMS FMP. This
process was initiated with the
publication of the draft Atlantic HMS 5
Year Review on March 5, 2015 (80 FR
11981). In this review, NMFS identified
new literature and data that should be
considered in EFH delineation
exercises, and recommended updating
boundaries for shortfin mako sharks.
There was insufficient information
available per the guidelines listed at
§ 600.815(a)(8)) to warrant a Habitat
Area of Particular Concern for shortfin
mako sharks. NMFS published a draft
Environmental Assessment, which
included proposed updates for shortfin
mako shark EFH, on September 8, 2016
(81 FR 62100). NMFS received a number
of written comments and comments at
public meetings. Many comments
included suggestions for EFH
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5361
boundaries based on academic research.
NMFS completed a review of EFHrelated literature in developing the FEIS
(see Chapter 3 and Chapter 4 of
Amendment 10 for a review of shortfin
mako habitat and biology, and EFH
impacts, respectively), and did not
identify sufficient literature warranting
changes to the recently updated EFH
boundaries for shortfin mako sharks.
However new data from ongoing
surveys, research, and tagging programs
was used to update EFH boundaries.
EFH updates for shortfin mako sharks
were finalized September 6, 2017 (82 FR
42329). Maps of final EFH boundaries
for shortfin mako are available in
Appendix G of the Final Environmental
Assessment. EFH boundaries may also
be viewed in the EFH Mapper, an online
dynamic mapping tool maintained by
the NMFS Office of Habitat
Conservation (https://
www.habitat.noaa.gov/protection/efh/
efhmapper/). This office also maintains
an EFH Data Inventory, which includes
shapefiles of EFH boundaries that may
be downloaded by the public (https://
www.habitat.noaa.gov/protection/efh/
newInv/). The next 5-year
review process for HMS EFH will be
initiated in 2022.
Comment 7: NMFS received several
comments suggesting that management
measures for shortfin mako sharks
should be more restrictive than those
implemented in this rulemaking,
including prohibiting all retention of
shortfin mako sharks, or other more
restrictive measures, as the science
recommends.
Response: NMFS disagrees that more
restrictive measures are required or
necessary at this time. The management
measures in Amendment 11 are
consistent with those recommended in
ICCAT Recommendation 17–08 and
with NMFS’ obligations to address
overfishing and rebuilding,
understanding that the stock is fished
internationally and requires
international measures to effectively
address these issues. The selected
measures are expected to reduce U.S.
shortfin mako shark catch consistent
with the SCRS recommendation (72–79
percent), while still permitting
fishermen to retain shortfin mako sharks
under limited circumstances. Given the
species’ North Atlantic-wide range and
that United States catches constitute
only approximately nine percent of total
North Atlantic shortfin mako shark
catch, the United States cannot
unilaterally end overfishing and rebuild
the stock through domestic regulations
alone, even if there were to be a total
prohibition on possession (which has
not been recommended by ICCAT).
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Ending overfishing and rebuilding the
stock can only be accomplished through
international coordination with nations
that harvest the majority of shortfin
mako sharks. NMFS will work with
ICCAT members to evaluate the
effectiveness of these measures, update
stock assessment projections, establish a
rebuilding plan, and develop additional
measures if necessary.
Comment 8: NMFS received
comments in support of the proposed
preferred commercial alternative (A2),
as well as other comments that
suggested modifications to Alternative
A2. Several commenters along with the
State of Georgia and the South Atlantic
and New England Fishery Management
Councils supported Alternative A2 (the
preferred Alternative at the proposed
rule stage) since this Alternative is
consistent with ICCAT
Recommendation 17–08, utilized
electronic monitoring, and allowed
NMFS to collect real time landings and
additional data. NMFS also received
comments including from the State of
North Carolina, Commonwealth of
Massachusetts, and HMS Advisory
Panel members supporting Alternative
A2 with modifications. Specifically, the
State of North Carolina along with other
individuals suggested a modification
that would allow the retention of dead
shortfin mako sharks caught as bycatch
in gillnet and bottom longline fisheries.
The Commonwealth of Massachusetts
and some HMS Advisory Panel
members suggested a modification that
would allow the retention of dead
shortfin mako sharks by any vessel as
long as there is an electronic monitoring
system or an observer on board the
vessel, similar to Alternative A5. These
commenters also supported Alternative
A3, which would allow vessels the
option to opt out of the electronic
monitoring system review.
Response: ICCAT Recommendation
17–08 included a variety of measures to
reduce shortfin mako shark fishing
mortality and to increase live releases in
response to the 2017 ICCAT North
Atlantic shortfin mako shark stock
assessment. Among these measures was
the option to require the release of
shortfin mako sharks brought to the
vessel alive in ICCAT fisheries. This
option also allows for the retention of
shortfin mako sharks in ICCAT fisheries
that are dead at haulback, provided an
electronic monitoring system is
installed, or an observer is on board to
verify the disposition of the shark. In
Draft Amendment 11, NMFS preferred
to implement Alternative A2, which
limited the retention of dead shortfin
mako sharks to those caught on vessels
with an electronic monitoring system.
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While the draft amendment preferred
alternative did not limit the gear types
that could be used to catch and retain
dead shortfin mako sharks, the
requirement to have an electronic
monitoring system installed largely
limited the measure to pelagic longline
vessels since these vessels are already
required to have electronic monitoring
systems. Alternative A2 would satisfy
the requirements of Recommendation
17–08 and also decrease fishing
mortality of shortfin mako sharks. A
large number of commenters expressed
support for this measure. A full analysis
of the ecological and socioeconomic
impacts for Alternative A2 is provided
in Chapter 4 of the FEIS.
However, during the public comment
period, commenters that expressed
support for the preferred Alternative A2
in Draft Amendment 11 also voiced
support for allowing retention of dead
shortfin mako sharks in other, nonICCAT fishery gear types. Although
Alternative A2 did not limit the ability
to retain dead shortfin mako sharks to
pelagic longline vessels, the
requirement to install a costly electronic
monitoring system to do so may have
effectively limited the allowance for
retention to the pelagic longline fishery.
HMS-permitted pelagic longline vessels
are already required to have electronic
monitoring systems on board, but
vessels using other gear types are
unlikely to install the costly system in
order to retain shortfin mako sharks,
especially considering the relatively low
ex-vessel value. Thus, the practical
effect of Alternative A2 could be to limit
the measure to pelagic longline vessels.
To address the public comments on the
Proposed Rule for Amendment 11,
NMFS is implementing Alternative A7,
an alternative added and analyzed in
the FEIS and adopted in this final rule.
Alternative A7 is a slight modification
and outgrowth of Alternative A2. Under
preferred Alternative A7, shortfin mako
sharks caught using gillnet, bottom
longline, or pelagic longline gear on
properly-permitted vessels could be
retained, provided they are dead at
haulback. In the case of pelagic longline
vessels, an electronic monitoring system
would still be required, as proposed, but
an electronic monitoring system would
not be required on vessels that use
bottom longline or gillnet gear. To be
responsive to public comments, NMFS
reviewed the available data for shortfin
mako shark interactions by vessels that
use bottom longline and gillnet gear.
After reviewing the information and
considering past actions, NMFS decided
to add Alternative A7 as the preferred
alternative. One of the alternatives in
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the proposed rule analyzed and
considered retention within the bottom
longline and gillnet fisheries, and public
comment on the alternatives resulted in
the development of Alternative A7.
Commenters thus could reasonably have
anticipated this alternative, which is a
logical outgrowth of the alternatives
considered, and is consistent with the
ICCAT measure’s application to sharks
‘‘caught in association with ICCAT
fisheries.’’ This alternative is largely the
same as Alternative A2 except that it
allows retention of dead shortfin mako
sharks in the bottom longline and the
gillnet fisheries without requiring an
observer or electronic monitoring
system on board. Shortfin mako sharks
are rarely caught with bottom longline
and gillnet gear. Based on observer data,
only 40 shortfin mako sharks were
caught with bottom longline and gillnet
gear from 2012 to 2017. Due to the low
number of observed interactions, it is
doubtful any of these landings were the
result of targeted fishing so it is unlikely
more could be done to avoid them.
NMFS will also continue to track
landings and consider additional
measures if it appeared that an increase
in retention results from this action,
which is extremely unlikely. Retaining
an additional six to seven dead sharks
per year will have no additional
negative effects on the stock than
considered in the proposed rule, and the
United States will still achieve the
needed reductions in mortality with this
alternative. In addition, allowing
retention by these gear types will reduce
regulatory dead discards in the nonICCAT fisheries.
No other commercial gear types
would be able to land shortfin mako
sharks under this alternative. While it is
possible for other commercial gears to
catch shortfin mako sharks (e.g., rod and
reel and bandit gear), these gears are
primarily recreational and are rarely
used to fish for sharks commercially.
Buoy gear in particular can interact with
shortfin mako sharks but is not an
authorized gear; this rule does not
change that. Under this alternative, all
shortfin mako sharks would need to be
released if caught commercially on
these other commercial gears, with the
exception described below for those
vessels that hold both a commercial
shark permit and a permit with a shark
endorsement that allows for recreational
shark landings. This approach is
consistent with previous rulemakings
that implemented ICCAT
recommendations for sharks (e.g.,
prohibiting retention of silky,
hammerhead, oceanic whitetip, or
porbeagle sharks in ICCAT fisheries: 76
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FR 53652, August 29, 2011; 77 FR
60632, October 4, 2012; 81 FR 57803,
August 24, 2016). In those cases, NMFS
applied ICCAT measures for sharks only
to the pelagic longline fishery and the
handgear fisheries when swordfish or
tunas are retained because they are
considered ICCAT fisheries for tunas
and tuna-like species. NMFS
consistently determined that U.S.
bottom longline and gillnet vessels are
not part of an ICCAT fishery because
these gears do not regularly catch or
land ICCAT managed species such as
swordfish or tunas. In other words,
Alternative A7, which would allow
landings of dead shortfin mako sharks
caught by these non-ICCAT fishery gear
types, is consistent with past U.S.
actions.
Additionally, ICCAT
Recommendation 17–08 allows
retention of shortfin mako sharks that
are dead at haulback without the
verification of electronic monitoring or
observers in certain limited
circumstances, including for vessels
under 12 meters. Most vessels that have
a Directed shark LAP and use bottom
longline or gillnet gear have vessel
lengths that are below 12 meters. In
2017, bottom longline vessels that
interacted with sharks (based on coastal
fisheries and HMS logbook reports)
averaged 11.4 meters in length. In 2017,
gillnet vessels that interacted with
sharks (based on coastal fisheries and
HMS logbook reports) averaged 9.6
meters in length. Thus, given past
rulemakings and given the length of
most vessels that target sharks, allowing
landings of dead shortfin mako sharks
by these other gear types is appropriate
and consistent with ICCAT
Recommendation 17–08.
Comment 9: NMFS received a
suggestion for potential management
measures if more commercial
regulations are needed to protect the
shortfin mako stock. The commenter
suggested that NMFS implement a
seasonal incidental limit of 18 shortfin
mako sharks per trip during the summer
months.
Response: The preferred alternatives
in Final Amendment 11 are consistent
with ICCAT Recommendation 17–08
and are designed to address the United
States’ contribution to the overfishing of
shortfin mako sharks. If future ICCAT
SCRS analyses determine that
additional shortfin mako shark mortality
reductions are needed, NMFS would
consider other options, consistent with
any ICCAT recommendations. At this
time, a seasonal commercial limit of
shortfin mako sharks is not consistent
with ICCAT Recommendation 17–08
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and it is unclear if it would achieve
mortality reduction targets.
Comment 10: NMFS received a
comment that the combination of
preferred alternatives at the proposed
rule stage, specifically Alternatives A2
and B3, would cause commercial shark
permits that are held with HMS Charter/
Headboat permits to be ‘‘worthless.’’
Such fishermen hold both permits to
allow them to sell sharks caught as
bycatch when fishing for tuna with
handline gear. The proposed
combination of alternatives would
require such a dual-permitted vessel to
use only pelagic longline gear, to have
an electronic monitoring system, and to
only land shortfin mako sharks that
were greater than 83 inches fork length
that were dead at haulback. These
requirements would apply even when
fishing on a for-hire trip.
Response: The commenter was correct
that under the proposed alternatives it
was unlikely that a dual-permitted
vessel (which could include a variety of
permits including, for example, those
vessels that hold a commercial shark
permit and an Atlantic Tunas General
category permit that allows for retention
of sharks when participating in a
registered tournament) could land
shortfin mako sharks. Additionally,
NMFS realized this concern about
permit combinations could apply to
many combinations of the commercial
and recreational alternatives considered.
NMFS did not intend for this effect as
a result of the proposed rule. As such,
in the FEIS, NMFS is clarifying how the
recreational limits would apply to the
few individuals who hold a commercial
shark vessel permit in addition to one
of a variety of other vessel permits, such
as HMS Charter/Headboat, that allow for
recreational landings of sharks. These
vessels generally fish with rod and reel
or other handgear as opposed to pelagic
longline, bottom longline, or gillnet
gear. However, these vessels are part of
the ICCAT fishery as they regularly
target tunas, billfish, and swordfish. For
the sake of clarity, NMFS would restrict
these permit holders to the recreational
shark requirements when shortfin mako
sharks are onboard and prohibit them
from selling any sharks when
recreationally retaining shortfin mako
sharks.
Comment 11: NMFS received
comments both in support of and
opposed to Alternative B3, which was
the preferred alternative at the proposed
rule stage. Some commenters, along
with the Commonwealth of
Massachusetts and the New England
Fishery Management Council,
supported Alternative B2 and
management measures to protect
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shortfin mako sharks until they reach
maturity. These commenters generally
felt that the United States strongly
supported the adopted size restrictions
at ICCAT, and that NMFS should not
now go beyond the recommendations.
These commenters noted that the same
minimum size under the emergency rule
reduced U.S. landings beyond the
suggested reduction of 72 to 79 percent.
Other commenters noted that NMFS
underestimated potential reductions in
landings in their analysis of the
recreational alternatives because they
did not account for reductions in the
number of trips that would target
shortfin mako sharks. The State of North
Carolina supported Alternative B3 and
specifically noted that if NMFS chooses
Alternative B2 instead, NMFS should
include shark sex identification facts on
the HMS shark endorsement quiz and
other outreach material. Commenters
from the Gulf of Mexico supported
Alternative B3 because they commonly
interact with shortfin mako sharks larger
than 83 inches fork length (FL). NMFS
also received comments from
individuals as well as the State of
Georgia and the South Atlantic Fishery
Management Council in support of the
Alternative B3, which would establish a
single recreational size limit of 83
inches FL, and is consistent with the
measure established in the emergency
rule. In general, these commenters felt
the one size limit in Alternative B3
would remove any confusion
recreational fishermen may have in
identifying shortfin mako sharks by sex.
Additionally, NMFS received requests
for NMFS to consider other minimum
sizes that are smaller than the preferred
alternative of 83 inches FL. These
commenters felt that NMFS should
protect the larger, breeding female
sharks over 83 inches FL and implement
a smaller minimum size, such as 72 or
75 inches FL, for male sharks since
those sharks still provide a decent
amount of meat.
Response: Based on the public
comment and current recreational
estimated harvest under the emergency
regulations (83 inches FL for all shortfin
mako sharks), NMFS has decided to
change the preferred alternative in the
Final Amendment 11 to Alternative B2,
which establishes different minimum
sizes for male and female shortfin mako
shark retention (71 inches FL size limit
for male and 83 inches FL size limit for
female shortfin mako sharks). In Draft
Amendment 11 and the emergency
interim final rule, the minimum size
limit was increased to 83 inches FL for
both males and females (Alternative B3)
to significantly reduce shortfin mako
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shark recreational mortality and address
overfishing. One size was used for both
sexes for reasons discussed in the
emergency interim final rule and
proposed rule. Updated data gathered
from operations occurring under the
emergency interim rule provisions
indicate, however, that this approach
would be unnecessarily restrictive for
the longer term. While the shortfin
mako shark landings under the 83-inch
FL size limit met the suggested
reduction target by weight, the size limit
exceeded the target reduction in
numbers of sharks harvested. As
described in Chapter 4 of the FEIS,
Large Pelagics Survey (LPS) data
indicated there was a substantial
reduction in recreational trips targeting
shortfin mako sharks as a result of
implementation of the emergency
interim rule. The recreational landings
data observed in the LPS suggest that
the separate size limits for male and
female sharks now preferred under
Alternative B2 should still accomplish
the suggested mortality reduction targets
while having less detrimental economic
impacts on the recreational shark
fishery.
Furthermore, studies have indicated
that protecting sub-adult sharks is key to
conserving and rebuilding shark
populations (see Chapter 4 of the FEIS).
Sub-adults are generally those juvenile
sharks that are a year or two away from
becoming mature adults. While the
now-preferred Alternative B2 will allow
greater harvest of male shortfin mako
sharks, those sharks will still be mature
individuals as 71 inches FL is the size
of maturity for male shortfin mako
sharks. Given that studies have
indicated that protecting sub-adult
sharks is key to conserving and
rebuilding shark populations,
Alternative B2 ensures that sub-adults
would still be adequately protected by
establishing minimum size limits for
male and female sharks based on their
size at maturity. NMFS also anticipates
that the now-preferred Alternative B2,
which allows recreational fishermen the
opportunity to harvest smaller male
sharks, will help relieve fishing pressure
on the larger female sharks, which were
estimated to comprise approximately 75
percent of the harvest under the
preferred alternative from the
emergency interim final rule
(Alternative B3), which established only
one size for both males and females.
Landings data from the LPS shows that
female shortfin mako sharks over 83
inches FL historically made up only
about 12 percent of the overall harvest.
Under a single 83 inches FL size limit
it is highly likely most vessels that
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successfully harvest a shark over 83
inches FL will have already caught and
released several smaller male sharks
first. Since recreational fishermen are
only allowed to harvest one shortfin
mako shark per vessel per day,
establishing a separate and significantly
smaller size limit for male sharks will
greatly increase the probability that the
first legal sized shark a vessel interacts
with will thus be a male shark which
should lead to fewer female sharks
ultimately being harvested.
Since the final preferred alternative
(Alternative B2) establishes a different
minimum size limit for each sex of
shortfin mako shark species, NMFS
intends to include information on
properly distinguishing between male
and female sharks on all related
outreach materials, web page, and the
shark endorsement video (which is
mandatory for all HMS permit holders
that wish to retain sharks
recreationally). NMFS also expects to
provide such information to registered
HMS shark tournaments to make sure
participants are aware of the separate
size limits and how to distinguish
between male and female sharks. NMFS
will continue to monitor recreational
landings of shortfin mako sharks, and
would take action to increase the
minimum size limit if recreational
landings targets are not meet or if
enforcing separate size limits by sex
proves to be impractical.
Comment 12: NMFS received a
comment stating that the seasonal
recreational alternatives would not
allow Gulf of Mexico fishermen ample
opportunity to land shortfin mako
sharks since they primarily target the
species outside of the months
considered in the alternative.
Response: NMFS did not prefer
Alternative B6, or any of its subalternatives, in the proposed rule due to
the potential for inequitable fishing
opportunities this alternative could
create in terms of regional access to the
shortfin mako shark recreational fishery.
NMFS now prefers Alternative B2,
which establishes a minimum size limit
of 71 inches FL for male and 83 inches
FL for female shortfin mako sharks,
which would mean all recreational
fishermen would have the same
regulations regardless of where and
when they decide to fish.
Comment 13: NMFS received
comments in support of the no action
recreational alternative (Alternative B1).
Specifically, commenters supported
keeping the shortfin mako shark
recreational minimum size at status quo
(54 inches FL) since they feel the
population decline is not due to the
recreational fishery and the recreational
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fishery should not be impacted by other
fisheries.
Response: While NMFS recognizes
that the U.S. recreational fishery for
shortfin mako sharks only makes up a
small portion of the overall
international harvest, its contribution to
the total U.S. catch is larger than the
commercial fishery landings. According
to data presented in the Final
Amendment 11, the U.S. recreational
fishery accounts on average for 58
percent of the total U.S. catch, while the
commercial fishery accounts on average
for 42 percent. Therefore, U.S.
recreational fisheries have a significant
role to play in reducing fishing
mortality on shortfin mako sharks, and
must be included in management of this
overfished stock. Furthermore, the no
action alternative would fail to meet the
minimum requirements set forth in
ICCAT Recommendation 17–08 and
would be inconsistent with U.S.
obligations under the ICCAT treaty,
ATCA, and other legal requirements.
Comment 14: NMFS received
comments in support of Alternative B8,
which would establish a tagging
program to implement a per season limit
for recreational fishermen.
Response: At this time, NMFS does
not intend to implement a tagging
program for recreationally harvested
shortfin mako sharks since the final
preferred alternative (Alternative B2) to
establish minimum sizes would
sufficiently reduce the recreational
harvest levels. In addition, tagging
programs are complicated to implement
for a variety of reasons including the
need to assign a limited number of tags
via raffle, and the extra time and
resources required to track them when
reported. As discussed in the FEIS,
NMFS would need to assign tags via
raffle as the number of HMS permit
holders with shark endorsements far
exceeds the number of shortfin mako
sharks that could be harvested and still
meet the recommended reduction target
of 72 to 79 percent. For these reasons,
NMFS does not prefer a tagging program
at this time.
Comment 15: NMFS received a
comment suggesting that we change the
shortfin mako shark recreational fishery
to be similar to the bluefin tuna
recreational fishery regulations. The
commenter suggested a shortfin mako
shark recreational fishery where permit
holders would be restricted to one
trophy shark over 83 inches FL, one
smaller shark between 65 to 83 inches
FL, and a 2 shark per season limit per
recreational shark permit.
Response: The management regime
suggested in this comment would be
similar to the implementation of a
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tagging program in that such a program
would require NMFS to monitor a
seasonal bag limit. Similar to the tagging
program, NMFS has determined that
such a management program is
unnecessary to accomplish the
recommended reduction in landings as
the minimum size limits currently
under consideration would reduce
overall harvest to far fewer than two
sharks per permitted vessel per season.
Furthermore, a 65 inch FL size limit for
shortfin mako sharks would be below
the size limits stipulated in ICCAT
Recommendation 17–08, and would fail
to meet U.S. obligations to implement
binding ICCAT recommendations under
ATCA.
Comment 16: NMFS received support
and opposition for the preferred
alternative (Alternative B9) to
implement circle hooks in the
recreational fishery. Some commenters
along with the Commonwealth of
Massachusetts and the South Atlantic
and New England Fishery Management
Councils supported the preferred
alternative due to the benefits of live
release of sharks that may provide
enhanced survivorship in some species.
The State of Georgia opposed the
implementation of circle hooks in the
recreational fishery for sharks in federal
waters due to its ‘‘questionable
administration by law enforcement
officers’’ and the unnecessary burden it
will place on recreational anglers. In
addition, the State of Georgia noted that
it does not intend to adopt circle hooks
in state waters.
Response: Research shows that the
use of circle hooks reduces gut-hooking
and increases post-release survival in
shortfin mako sharks. French et al.
(2015) examined the effects of
recreational fishing techniques,
including hook type, on shortfin mako
sharks and found that circle hooks were
more likely to hook shortfin mako
sharks in the jaw compared to J-hooks.
In the study, circle hooks were most
likely to hook in the jaw (83 percent of
the time) while J-hooks most commonly
hooked in the throat (33 percent of the
time) or gut (27 percent of the time). Jhooks only hooked in the jaw of shortfin
mako sharks 20 percent of the time. Jawhooking is correlated with increased
odds of post release survival. For these
and other reasons (e.g., endangered
species interactions), NMFS prefers this
alternative. In addition, circle hooks are
already required by HMS permitted
commercial and recreational, except for
north of 41°43′ N latitude (near
Chatham, Massachusetts), fishermen.
While NMFS recognizes the State of
Georgia’s concern regarding
enforceability, circle hooks have been
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required by HMS recreational permit
holders since January 1, 2018, and other
states, such as the State of New York,
also requires the use of circle hooks
when fishing for sharks. In Amendment
5b to the 2006 Consolidated HMS FMP,
NMFS required the use of non-offset,
non-stainless steel circle hooks by HMS
recreational permit holders with a shark
endorsement when fishing for sharks
recreationally, except when fishing with
flies or artificial lures, in federal waters
south of 41°43′ N latitude (near
Chatham, Massachusetts). The final
preferred Alternative (Alternative B9)
would remove this line and require
circle hooks when fishing recreationally
for sharks in all areas, except when
fishing with flies or artificial lures.
Comment 17: NMFS received a
comment inquiring whether the new
MRIP estimates would impact this
rulemaking or future stock assessment.
Response: Recently, NMFS released
new MRIP effort and catch estimate time
series following the implementation of
the new Fishing Effort Survey (FES)
designed for the collection of private
boat and shore-based fishing effort data,
and its calibration with the data
collected by the historic Coastal
Household Telephone Survey (CHTS).
The implications of the revised
estimates on all managed species will
not be fully understood for several years
until they make their way through the
rigorous scientific stock assessment
process. In the coming years, the new
and revised data will be incorporated
into stock assessments at the domestic
and international level as appropriate.
However, NOAA Fisheries’ primary
source of recreational catch data for
shortfin mako sharks is the Large
Pelagic Survey (LPS) which does not
rely on the FES, and as a result the
estimates generated by the LPS used in
this rulemaking have not changed.
Comment 18: NMFS received a
comment stating that banning
tournament fishing for sharks would
help to end overfishing, and that NMFS
would be justified in doing so on the
grounds that tournament awards add a
commercial component to what is
supposed to be a recreational fishery.
The commenter also stated that
recreationally harvested fish should
only be used for personal consumption,
and not monetized.
Response: While tournaments do
make up a significant portion of the
recreational shark fishery, NMFS is not
in favor of prohibiting shark
tournaments as a means to address
overfishing of shortfin mako sharks for
a number of reasons. First, tournaments
can provide significant economic
benefits to the coastal communities in
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which they are held. Second, banning
tournament or sport fishing while still
allowing recreational harvest would
constitute an inequitable access of the
resource to the problem of overfishing
between tournament and nontournament recreational fishermen, and
would set a precedent that would
conflict with the management of other
U.S. fisheries. Retention of HMS,
including shortfin mako sharks
submitted for weigh-in to tournaments,
is authorized under the regulations by
the permitted vessel that caught the fish.
Even in cases where anglers donate their
fish to the tournament, the tournament
is not allowed to sell the fish, but may
only donate the fish for human
consumption to food banks or other
charities.
For HMS fisheries, most tournament
participants hold recreational permits or
commercial permits that only allow for
recreational landings of sharks when
used during a registered HMS
tournament. None of these participants
are allowed to sell their catch. Many
commercial businesses are associated
with recreational fisheries including forhire vessels, bait and tackle shops, and
fishing guides. Like tournaments, all of
these operations service recreational
anglers. The distinction between
recreational and commercial fishing lies
solely in whether the fish themselves
are sold commercially, not in whether a
business associated with an activity is
providing a commercial service. Many
shark tournaments are already moving
to catch-and-release formats, or are
shying away from targeting shark
species that are not widely considered
to be edible.
Comment 19: NMFS received support
and opposition for the preferred
alternative of no action Alternative C1.
Some commenters along with the
Commonwealth of Massachusetts, State
of Georgia, and South Atlantic Fishery
Management Council supported the
preferred alternative since it would not
add any additional reporting
requirements for fishermen. However,
commenters also were concerned that
some registered HMS tournaments are
currently not required to report their
catches of all HMS. Some commenters
opposed the preferred alternative since
it would create inconsistency with the
SCRS advice to gather more data and
information on shortfin mako sharks
and therefore would negatively impact
science and stock assessments. Some
individuals along with the Mid-Atlantic
Fishery Management Council suggested
that NMFS should implement
mandatory reporting for all
recreationally landed and discarded
shortfin mako sharks. The Mid-Atlantic
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Fishery Management Council stated that
it is imperative to collect data from
commercial and recreational fishermen
on landings and discards. Other
commenters would like equivalent
monitoring and accountability
requirements for all U.S. HMS fisheries,
and to fully and accurately account for
all sources of fishing mortality.
Response: There are already a number
of reporting requirements under current
HMS regulations for commercial and
recreational fishermen fishing for
shortfin mako sharks. HMS commercial
fishermen report shortfin mako shark
catches through vessel logbooks along
with dealer reporting of landings. Under
Alternative C1, HMS recreational
anglers fishing from Maine to Virginia
would continue to be required to report
shortfin mako shark landings and
releases if intercepted by the LPS, and
data would continue to be collected on
shortfin mako shark catches by the
APIS, which is part of MRIP. As of
January 1, 2019, all registered HMS
tournaments will be selected for
tournament reporting, which should
account for a significant component of
recreational shortfin mako shark
landings (83 FR 63831; December 12,
2018). In addition, most for-hire vessels
fishing in the federal waters in the MidAtlantic area (New York to New
Carolina) are currently required by the
Mid-Atlantic Fishery Management
Council to submit electronic vessel trip
reports for all their trips within 24
hours, thus providing another major
data stream for shortfin mako shark
landings. These current reporting
systems will allow NMFS to effectively
monitor the recreational harvest of the
stock using a combination of traditional
intercept surveys, tournament reporting,
and electronic reporting making the
implementation of mandatory 24-hour
reporting unnecessary at this time.
NMFS understands that some
constituents do not think there is
equitable reporting across HMS
fisheries; however, the current reporting
systems mentioned above should
account for all sources of fishing
mortality for shortfin mako sharks.
NMFS will continue to monitor the
landings by commercial and
recreational fishermen to determine if
the current reporting systems are
sufficiently accounting for shortfin
mako shark mortality.
Comment 20: NMFS received a
comment in support of requiring
mandatory reporting with vessel
monitoring systems (VMS) if it would
simplify commercial fishermen’s
reporting burden, improve the reporting
of HMS catches across all gears, and
improve scientific data. The
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commenters were not supportive of the
alternative that would create another
unnecessary burden on commercial
fishermen.
Response: NMFS agrees that requiring
mandatory reporting of shortfin mako
sharks via VMS could potentially, and
unnecessarily, increase burden to HMS
commercial vessels that already report
in other ways (vessel logbooks, dealer
reports of landings, and electronic
monitoring system) that are sufficient
reporting systems for improving data
collection for shortfin mako sharks. In
addition, given the current reporting
requirements for all HMS commercial
vessels that already enable inseason
monitoring and management of shortfin
mako sharks, NMFS did not prefer this
alternative at this time. Furthermore,
NMFS is already implementing
electronic HMS logbooks on a voluntary
basis to improve the timeliness of
reporting, and provide data for
management.
Comment 21: NMFS received support
and opposition for the preferred
alternative. Some commenters along
with the Commonwealth of
Massachusetts, the State of Georgia, and
the South Atlantic and Mid-Atlantic
Fishery Management Councils
supported the preferred alternative to
develop an international rebuilding plan
with ICCAT to assist with rebuilding the
stock and work with other countries to
implement international management
measures. A commenter who opposed
the preferred alternative wants NMFS to
implement a domestic rebuilding plan
along with the international plan, while
other commenters prefer that NMFS
wait until ICCAT takes further action
before finalizing the rebuilding plan.
Response: North Atlantic shortfin
mako shark distribution spans a large
portion of the North Atlantic Ocean
basin and many countries besides the
United States interact with the species.
Therefore, NMFS believes that
addressing overfishing and preventing
an overfished status can only effectively
be accomplished through international
efforts where other countries that have
large landings of shortfin mako sharks
actively and equitably participate in
mortality reduction and rebuilding plan
discussions. Because of the small U.S.
contribution to North Atlantic shortfin
mako shark mortality, domestic
reductions of shortfin mako shark
mortality alone would not end
overfishing of the entire North Atlantic
stock. For these reasons and for the
reasons described in response to
comment 3 above, NMFS prefers
Alternative D3, which would establish
the foundation for developing an
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international rebuilding plan for
shortfin mako sharks.
Comment 22: NMFS received a
comment in support of the alternative to
remove shortfin mako sharks from the
pelagic shark management group and
establish a separate management group
with quota for the species.
Response: At this time, NMFS does
not prefer a shortfin mako shark-specific
quota. ICCAT Recommendation 17–08
did not include individual country
allocations for shortfin mako sharks
upon which to base a domestic quota. It
is also not clear that a quota would
adequately protect the stock by reducing
mortality because quotas allow for
sharks that are live at haulback to be
landed. Also, it is difficult at this time
to determine if setting a species-specific
quota for shortfin mako sharks would
have positive ecological benefits for the
stock, as this scenario was not explored
in the stock assessment. A speciesspecific quota for shortfin mako sharks
would require authorized fishermen to
discard all shortfin mako sharks once
the quota is reached, potentially leading
to an increase in regulatory discards,
which would not result in decreased
mortality of shortfin mako sharks and
thus, contribute to the health of the
stock. Additionally, commercially,
shortfin mako sharks are most often
caught with pelagic longline gear
incidental to other target catch. Since
shortfin mako sharks are rarely targeted,
establishing a shortfin mako shark quota
is unlikely to stop incidental fishing
mortality.
NMFS believes that ending
overfishing and preventing an
overfished status would be better
accomplished through the measures
preferred in final Amendment 11 and
through further critical international
efforts where other countries that have
large landings of shortfin mako sharks
could participate in mortality reduction
discussions instead of a species-specific
quota within the U.S. fisheries. NMFS
will continue to monitor progress in the
international forum and the needs of the
stock, as well as whether this action has
its intended effect, and will consider
whether additional measures are
appropriate in the future.
Comment 23: NMFS received a
comment in support of the alternative to
establish bycatch caps for all fisheries
that interact with shortfin mako sharks.
Specifically, the commenter noted that
NMFS should count the number of
shortfin mako sharks caught in all
fisheries, cap the number of shortfin
mako sharks that can be caught, and
implement accountability measures to
control, track, and limit the number of
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shortfin mako sharks that are killed in
each fishery.
Response: At this time, NMFS does
not prefer bycatch caps for all fisheries
that interact with shortfin mako sharks.
NMFS has reviewed all data available
and found that shortfin mako sharks are
primarily caught in HMS fisheries with
pelagic longline gear when commercial
fishermen are harvesting swordfish and
tuna species, and with rod and reel gear
when recreational fishermen are
targeting sharks or other HMS. The
species is rarely caught in other
fisheries or with other gear types. To the
extent they are, the final preferred
commercial alternative, Alternative A7,
limits any landing to shortfin mako
sharks that are dead at haulback.
Because shortfin mako sharks are rarely
seen in fisheries other than the ones
listed, establishing bycatch caps in nonpelagic longline or non-recreational
handgear fisheries is unlikely to provide
additional protection. As ICCAT has not
established an overall TAC for shortfin
mako sharks, it is difficult to determine
at what level NMFS would establish a
bycatch cap. Given that shortfin mako
sharks are rarely caught on these other
gear types, a bycatch cap would be
unlikely to change fishing behavior or
result in sufficient ecological benefits
that compensate for administrative and
regulatory burden. However, if shortfin
mako shark interactions increase in
those fisheries, which would then
indicate fishing behavior has changed in
some form, then NMFS may consider
additional measures such as
establishing a bycatch cap in these
fisheries in the future.
Comment 24: NMFS received a
comment suggesting that we increase
the minimum recreational size limit for
porbeagle sharks.
Response: This comment is beyond
the scope of this rulemaking. The
purpose of Amendment 11 is to develop
and implement management measures
that would address overfishing and take
steps towards rebuilding the North
Atlantic shortfin mako shark stock. The
most recent stock assessment for
porbeagle sharks indicated that the
stock was overfished, but overfishing
was no longer occurring, and showing
signs of early rebuilding. At this time,
NMFS does not have any new scientific
information to justify increasing the
minimum recreational size limit for
porbeagle sharks.
Changes From the Proposed Rule (83
FR 35590; July 27, 2018)
This section explains the changes in
the regulatory text from the proposed
rule to the final rule. Some changes
were made in response to public
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comment, and others clarify text for the
final rule. The changes from the
proposed rule text in the final rule are
described below.
1. § 635.20(e)(2) and (e)(6). Modification
to the Recreational Minimum Size Limit
for Shortfin Mako Sharks
This final rule implements separate
size limits for male (71 inches FL) and
female (83 inches FL) shortfin mako
sharks under Alternative B2 as opposed
to the single size limit of 83 inches FL
(Alternative B3) that was preferred in
the proposed rule and implemented in
the emergency interim final rule. NMFS
decided to change the preferred
alternative due to public comment and
updated data on the effects of the
emergency interim final rule measure on
estimated landings and directed effort
for shortfin mako sharks in the
recreational fishery. The minimum sizes
in the final rule also directly match the
measures in the ICCAT
recommendation, which provided
different minimum sizes for males and
females.
For the emergency interim rule and
the proposed rule, NMFS assumed in
the recreational analyses that directed
effort for shortfin mako sharks would
not change as a result of a change in the
minimum retention size, but the 2018
LPS data found that effort actually went
down substantially. Thus, NMFS now
understands the estimates of expected
landings reductions in the earlier
actions to be overly conservative.
Furthermore, public comment reflected
that fewer recreational trips were taken
due to the larger minimum size limit
and reduced likelihood of catching and
landing a shortfin mako shark above the
size limit. Thus, in the final rule, it is
appropriate to reduce the minimum size
limit for males to 71 inches FL,
consistent with the ICCAT
recommendation. The minimum size for
female mako sharks will remain at 83
inches FL.
The differing minimum size limits in
the preferred alternative are expected to
achieve the needed reduction in
landings and fishing mortality while
protecting reproductive-age female
shortfin mako sharks, but with fewer
socio-economic impacts to recreational
fishermen. By reducing the minimum
size for retaining male shortfin mako
sharks, fishermen may more frequently
harvest smaller, mature male sharks
instead of the larger female sharks,
which will leave more female sharks
that are critical to reproduction of the
stock in the population. This approach,
which reduces fishing pressure on the
female spawning stock, is consistent
with general scientific advice about
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sharks. (Cortes 2002, Chapple and
Botsford 2013).
According to length composition
information from the LPS from 2012
through 2017, this final action would
reduce the number of recreational
landings of male shortfin mako sharks
by up to 47 percent and female shortfin
mako sharks by up to 78 percent for an
average reduction in total morality of 65
percent, if fishing effort for shortfin
mako sharks were to remain the same.
However, the reduction in landings
under this alternative is likely to be
somewhat greater than that because
recreational fishermen likely will
continue taking fewer trips targeting
shortfin mako sharks as a result of the
changes in size limits. Effort data
collected via the LPS suggests that in
2018 there was a large reduction in
directed fishing trips targeting shortfin
mako sharks under the 83-inch FL size
limit implemented by the emergency
interim final rule compared to the
previous six-year average. Directed trips
in the LPS region (Maine to Virginia) for
shortfin mako sharks from June through
August 2018 declined an estimated 34
percent compared to the six-year
average from 2012 through 2017. This
reduction in directed trips resulted in
greater than projected reductions in
shortfin mako shark landings. The June
through August time period
traditionally accounts for over 90
percent of directed trips for shortfin
mako sharks. Based on the LPS data
from 2012 through 2017, shortfin mako
sharks were the primary target species
in approximately 67 percent of trips that
caught and 75 percent of trips that
landed the species. As such, a reduction
in directed fishing effort could
substantially reduce the landings
expected under this alternative, while
achieving the needed fishing mortality
reductions in conjunction with other
measures in the final rule.
As explained above in the comment
and response section, such reductions
in fishing effort should result in
landings reductions that more closely
result in the ICCAT reduction target of
72 to 79 percent than those that would
have resulted from the single 83-inch FL
size limit (Alternative B3), which
resulted in greater reductions. Thus,
NMFS is implementing two separate
size limits for shortfin mako sharks.
Public comment reflects that some
people are concerned about the ability
of recreational shark anglers to
differentiate between male and female
sharks. NMFS is adding information on
how to distinguish the sex of sharks in
shark outreach materials, including the
Shark Endorsement educational video
that all HMS permit holders must watch
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if they wish to receive a shark
endorsement needed to retain sharks
recreational.
2. §§ 635.21(a)(4), (c)(1), (d)(5), and
(g)(6); 635.24(a)(4); and 635.71(d)(27)
and (d)(28). Modification to Authorized
Commercial Gear To Retain Shortfin
Mako Sharks
The commercial measure preferred in
the proposed rule (Alternative A2) only
allowed the retention of shortfin mako
sharks that were dead at haulback by
vessels with a functioning electronic
monitoring system on board the vessel.
While the proposed measure did not
limit the gear types that could be used
to catch and retain dead shortfin mako
sharks, the requirement to have an
electronic monitoring system installed
effectively limited the measure to
pelagic longline vessels since those
vessels are already required to have
electronic monitoring systems. In
response to public comments, NMFS
reviewed the available data for shortfin
mako shark interactions by vessels that
use bottom longline and gillnet gear.
Available data indicates that allowing
fishermen to retain dead shortfin mako
sharks caught in bottom longline or
gillnet gear is unlikely to impact the
overall mortality or harvest totals, since
these gear types rarely interact with the
species. Specifically, commercial shark
fishermen using bottom longline or
gillnet gear rarely, if ever, catch shortfin
mako sharks. Since 2012, only six
shortfin mako shark were observed in
the bottom longline shark fishery and 34
were observed in the gillnet shark
fishery. ICCAT Recommendation 17–08
allows retention of shortfin mako sharks
that are dead at haulback without the
verification of electronic monitoring or
observers in certain limited
circumstances, including for vessels
under 12 meters. Most vessels that have
a shark LAP and use bottom longline or
gillnet gear have vessel lengths that are
below 12 meters. In 2017, bottom
longline vessels that interacted with
sharks (based on coastal fisheries and
HMS logbook reports) averaged 11.4
meters in length. In 2017, gillnet vessels
that interacted with sharks (based on
coastal fisheries and HMS logbook
reports) averaged 9.6 meters in length.
Thus, given past rulemakings and given
the length of most vessels that target
sharks, allowing landings of dead
shortfin mako sharks by these other gear
types is appropriate and consistent with
ICCAT Recommendation 17–08. As a
result, in the final rule, NMFS will
allow for the retention of shortfin mako
sharks that are dead at haulback by
properly-permitted vessels that are
fishing with bottom longline or gillnet
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gear even if they do not have a
functioning electronic monitoring
system on board. The changes in the
regulatory text specifies that vessels
with bottom longline or gillnet gear
onboard must release all live shortfin
mako sharks.
3. § 635.22(c)(1) and (c)(7).
Modifications Regarding Atlantic HMS
Charter/Headboat, Atlantic Tunas
General Category, and Swordfish
General Commercial Permit Holders
Based on public comment, NMFS is
clarifying how the recreational limits
would apply to the few individuals who
hold a commercial shark vessel permit
in addition to one of a variety of other
vessel permits, such as HMS Charter/
Headboat, that allow for recreational
landings of sharks under certain
circumstances. These individuals
generally fish with rod and reel or other
handgear as opposed to pelagic longline,
bottom longline, or gillnet gear. While
they hold a commercial shark permit,
for the most part, these individuals are
fishing for sharks recreationally.
However, under the combination of
measures in the proposed rule, these
individuals would not be allowed to
land any shortfin mako sharks as they
would not have the electronic
monitoring equipment required under
the proposed commercial measures. For
the sake of clarity and in response to
public comment, this rule specifies that
the recreational shark requirements,
including the no sale requirement,
apply for these individuals when
shortfin mako sharks are onboard.
Classification
Pursuant to the Magnuson-Stevens
Act, the NMFS Assistant Administrator
has determined that the final rule is
consistent with the 2006 Consolidated
HMS FMP and its amendments, other
provisions of the Magnuson-Stevens
Act, ATCA, and other applicable law.
The Assistant Administrator for
Fisheries, NOAA, finds good cause to
waive the 30-day delay in effective date
under 5 U.S.C. 553(d)(3) of the
Administrative Procedure Act. Delaying
the effectiveness of these regulations
could undermine the purpose of this
action to put in place measures to
address overfishing of shortfin mako
sharks. Similar measures were originally
implemented by emergency interim
final rule under Section 305(c) of the
Magnuson-Stevens Act, and have been
in place for since March 2018. The
emergency measures will expire on
March 3, 2019, and a lapse in these
measures would be confusing to the
regulated community, complicate
enforcement efforts, and potentially
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harm the long-term sustainability of the
stock. While NMFS originally timed the
rulemaking to allow for a delay in
effectiveness, a lapse in government
appropriations resulted in a government
shutdown for 35 days in December
2018–January 2019. If these measures
are not implemented before the
emergency rule expires, technically the
management measures for the stock
would revert to those that existed prior
to the emergency rule. This means the
recreational minimum size limit for
shortfin mako sharks would revert to 54
inches FL, the use of circle hooks by
recreational fishermen would not be
required across the range of the species
stock, and commercial fishermen would
no longer be required to release shortfin
mako sharks that are alive at haulback.
This would be confusing for the
regulated community, which would
then be required to switch to the new
regulations only 30 days later. In the
event of a short lapse between the
emergency rule and implementation of
this final rule, NMFS would notify the
regulated community of the situation
and encourage voluntary compliance
with the emergency rule measures for
consistency but compliance would not
be assured. Thus, the need to implement
these measures in a timely manner to
reduce the risk of overfishing shortfin
mako sharks constitute good cause to
make the rule effective immediately
upon publication in the Federal
Register. Furthermore, prior to the
release of this final rule, on December
14, 2018, NMFS published a notice of
availability of the Final EIS supporting
this action, thereby providing the public
and affected entities prior notice of the
final measures contained in this rule.
This final rule has been determined to
be not significant for purposes of
Executive Order 12866. The Agency has
consulted, to the extent practicable,
with appropriate state and local officials
to address the principles, criteria, and
requirements of Executive Order 13132.
In compliance with section 604 of the
Regulatory Flexibility Act (RFA), NMFS
prepared a Final Regulatory Flexibility
Analysis (FRFA) for this final rule. The
FRFA analyzes the anticipated
economic impacts of the final actions
and any significant economic impacts
on small entities. The FRFA is below.
Section 604(a)(1) of the RFA requires
a succinct statement of the need for and
objectives of the rule. Consistent with
the provisions of the Magnuson-Stevens
Act and ATCA, NMFS plans to modify
the 2006 Atlantic HMS FMP in response
to ICCAT Recommendation 17–08 and
the stock status determination for
shortfin mako sharks. NMFS has
identified the following objectives with
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regard to this action: Address
overfishing of shortfin mako sharks; take
steps towards rebuilding; establish the
foundation for rebuilding the North
Atlantic shortfin mako stock; and
modify the 2006 Consolidated HMS
FMP in response to ICCAT
Recommendation 17–08 and the stock
status determination for shortfin mako
sharks.
Section 604(a)(2) requires a summary
of significant issues raised by public
comment in response to the IRFA and
a summary of the assessment of the
Agency of such issues, and a statement
of any changes made in the rule as a
result of such comments. NMFS did not
receive any comments specifically on
the IRFA, however the Agency did
receive some comments regarding the
anticipated or perceived economic
impact of the rule. Summarized public
comments and the Agency’s responses
to them are included above. We did not
receive any comments from the Chief
Counsel for Advocacy of the Small
Business Administration in response to
the proposed rule or the IRFA.
Section 604(a)(4) of the Regulatory
Flexibility Act requires Agencies to
provide an estimate of the number of
small entities to which the rule would
apply. The Small Business
Administration (SBA) has established
size criteria for all major industry
sectors in the United States, including
fish harvesters. Provision is made under
SBA’s regulations for an agency to
develop its own industry-specific size
standards after consultation with SBA
Office of Advocacy and an opportunity
for public comment (see 13 CFR
121.903(c)). Under this provision,
NMFS may establish size standards that
differ from those established by the SBA
Office of Size Standards, but only for
use by NMFS and only for the purpose
of conducting an analysis of economic
effects in fulfillment of the agency’s
obligations under the RFA. To utilize
this provision, NMFS must publish such
size standards in the Federal Register
(FR), which NMFS did on December 29,
2015 (80 FR 81194, December 29, 2015).
In this final rule, effective on July 1,
2016, NMFS established a small
business size standard of $11 million in
annual gross receipts for all businesses
in the commercial fishing industry
(NAICS 11411) for RFA compliance
purposes. NMFS considers all HMS
permit holders to be small entities
because they had average annual
receipts of less than $11 million for
commercial fishing. The Small Business
Administration (SBA) has established
size standards for all other major
industry sectors in the U.S., including
the scenic and sightseeing
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transportation (water) sector (NAICS
code 487210, for-hire), which includes
charter/party boat entities. The Small
Business Administration (SBA) has
defined a small charter/party boat entity
as one with average annual receipts
(revenue) of less than $7.5 million.
Regarding those entities that would be
directly affected by the recreational
management measures, HMS Angling
(Recreational) category permits are
typically obtained by individuals who
are not considered businesses or small
entities for purposes of the RFA because
they are not engaged in commercial
business activity. Vessels with the HMS
Charter/Headboat category permit can
operate as for-hire vessels. These permit
holders can be regarded as small entities
for RFA purposes (i.e., they are engaged
in the business of fish harvesting, are
independently owned or operated, are
not dominant in their field of operation,
and have average annual revenues of
less than $7.5 million). Overall, the
recreational alternatives would have
impacts on the portion of the 3,635
HMS Charter/Headboat permit holders
who hold a shark endorsement. There
were also 287 registered HMS
tournaments in 2017, which could be
impacted by this rule. Of those
registered HMS tournaments, 75 had
awards or prizes for pelagic sharks.
Regarding those entities that would be
directly affected by the preferred
commercial management measures, the
average annual revenue per active
pelagic longline vessel is estimated to be
$187,000 based on the 170 active vessels
between 2006 and 2012 that produced
an estimated $31.8 million in revenue
annually. The maximum annual
revenue for any pelagic longline vessel
between 2006 and 2016 was less than
$1.9 million, well below the NMFS
small business size standard for
commercial fishing businesses of $11
million. Other non-longline HMS
commercial fishing vessels generally
earn less revenue than pelagic longline
vessels. Therefore, NMFS considers all
Atlantic HMS commercial permit
holders to be small entities (i.e., they are
engaged in the business of fish
harvesting, are independently owned or
operated, are not dominant in their field
of operation, and have combined annual
receipts not in excess of $11 million for
all its affiliated operations worldwide).
The preferred commercial alternatives
would apply to the 280 Atlantic tunas
Longline category permit holders, 220
directed shark permit holders, and 268
incidental shark permit holders. Of
these 280 permit holders, 88 pelagic
longline vessels were actively fishing in
2017 based on logbook records. Based
on HMS and Coastal Fisheries Logbook
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5369
data, an average of 20 vessels per year
that used gear other than pelagic
longline gear interacted with shortfin
mako sharks between 2015 and 2017.
NMFS has determined that the
preferred alternatives would not likely
directly affect any small organizations
or small government jurisdictions
defined under RFA, nor would there be
disproportionate economic impacts
between large and small entities.
Furthermore, there would be no
disproportionate economic impacts
among the universe of vessels based on
gear, home port, or vessel length.
Section 604(a)(5) of the RFA requires
agencies to describe any new reporting,
record-keeping and other compliance
requirements. The action does not
contain any new collection of
information, reporting, or recordkeeping requirements.
Section 604(a)(6) of the RFA requires
agencies to describe the steps taken to
minimize the significant economic
impact on small entities consistent with
the stated objectives of applicable
statutes, including a statement of the
factual, policy, and legal reasons for
selecting the alternative adopted in the
final rule and why each one of the other
significant alternatives to the rule
considered by the agency which affect
the impact on small entities was
rejected. Alternative A1, the No Action
alternative, would keep the nonemergency rule regulations for shortfin
mako sharks. Once the emergency rule
for shortfin mako sharks expires,
management measures would revert
back to those effective before March
2018 (e.g., no requirement to release
shortfin mako sharks that are alive at
haulback). Directed and incidental shark
LAP holders would continue to be
allowed to land and sell shortfin mako
sharks to an authorized dealer, subject
to current limits, including the pelagic
shark commercial quota. Short-term
direct economic impacts on small
entities would likely be neutral since
commercial fishermen could continue to
catch and retain shortfin mako sharks at
a similar level and rate as the status quo.
In recent years, about 181,000 lb dw
of shortfin mako sharks have been
landed and the commercial revenues
from shortfin mako sharks have
averaged approximately $373,000 per
year, which equates to approximately 1
percent of overall HMS ex-vessel
revenues. Approximately 97.5 percent
of shortfin mako commercial landings,
based on dealer reports, were made by
pelagic longline vessels. There were 88
pelagic longline vessels that were active
in 2017 based on logbook reports.
Therefore, the average revenue from
shortfin mako shark landings per
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pelagic longline vessel is $4,133 per
year.
Even though pelagic longline gear is
the primary commercial gear used to
land shortfin mako sharks, other gear
types also interact with this species.
Based on HMS and Coastal Fisheries
Logbook data, an average of 20 vessels
per year that used gear other than
pelagic longline gear interacted with
shortfin mako sharks between 2015 and
2017. Therefore, these vessels that used
gear other than pelagic longline gear
landed an average of only $933 worth of
shortfin mako sharks per year.
Under Alternative A2, retention of
shortfin mako sharks would only be
allowed if the following three criteria
are met: (1) The vessel has been issued
a Directed or Incidental shark LAP, (2)
the shark is dead at haulback, and (3)
there is a functional electronic
monitoring system on board the vessel.
This alternative is designed to be
consistent with one of the limited
provisions allowing retention of shortfin
mako sharks under ICCAT
Recommendation 17–08. Under the
current HMS regulations, all HMS
permitted vessels that fish with pelagic
longline gear are already required to
have a functional electronic monitoring
system (79 FR 71510; December 2, 2014)
and either a Directed or an Incidental
shark LAP. Vessels utilizing other gear
types (i.e., gillnet or bottom longline)
are not required to have an electronic
monitoring system under current
regulations but could choose to install
one if the operator wishes to retain
shortfin mako sharks that are dead at
haulback and if the vessel holds a
commercial shark LAP. Under this
alternative, the electronic monitoring
system would be used to verify and
ensure that only shortfin mako sharks
dead at haulback were retained.
This alternative would be consistent
with ICCAT Recommendation 17–08
and would reduce the number of
landings by pelagic longline vessels on
average by 74 percent based on observer
data from 2012–2017. A 74 percent
reduction in shortfin mako landings
would reduce revenues by an average of
$3,058 per vessel for the 88 activate
pelagic longline vessels and would
eliminate all of the $933 in landing per
vessel by the 10 non-pelagic longline
vessels that landing shortfin mako
sharks since those vessels are unlikely
to have electronic monitoring systems
currently installed. Those non-pelagic
longline vessels would need to pay to
install electronic monitoring systems if
they wish to retain shortfin mako
sharks, introducing an additional
expense for those vessels if it there were
an economic incentive for those vessels
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to try to retain shortfin mako sharks
under this alternative. Overall, this
alternative would have minor economic
costs on small entities because these
measures would reduce the number of
shortfin mako sharks landed and sold by
these fishing vessels. However, shortfin
mako sharks are rarely a target species
and are worth less than other target
species. Although this alternative was
preferred at the DEIS stage, NOAA
Fisheries now prefers Alternative A7
which is a slightly modified version of
Alternative A2. Because Alternative A7
is responsive to public comment while
still meeting management goals, NOAA
Fisheries no longer prefers Alternative
A2.
Alternative A3 is similar to
Alternative A2 except that the ability to
retain dead shortfin mako sharks would
be limited to permit holders that opt in
to a program that would use the existing
electronic monitoring systems, which
are currently used in relation to the
bluefin tuna IBQ program, also to verify
the disposition of shortfin mako sharks
at haulback. In other words, this
alternative would allow for retention of
shortfin mako sharks that are dead at
haulback by persons with a Directed or
Incidental shark LAP only if permit
holders opt in to enhanced electronic
monitoring coverage. If the permit
holder does not opt in to the enhanced
electronic monitoring coverage, they
could not retain any shortfin mako
sharks.
The economic impacts to small
entities under this alternative are
expected to be similar to those under
Alternative A2. Under this alternative, a
portion of the pelagic longline fleet
could opt out of any retention of
shortfin mako sharks, resulting in a
greater reduction in overall shark exvessel revenue for those vessels.
Overall, the socioeconomic impacts
associated with these reductions in
revenue are not expected be substantial,
as shortfin mako sharks comprise less
than one percent of total HMS ex-vessel
revenues on average. Non-pelagic
longline vessels would need to pay to
install electronic monitoring systems if
they wish to retain shortfin mako
sharks, introducing an additional
expense for those vessels. Due to the
low commercial value of shortfin mako
sharks and the high cost of electronic
monitoring it is reasonable to expect
that these fisheries will not install
cameras and therefore will not retain
shortfin mako sharks. Overall, this
alternative would have minor economic
costs on small entities by reducing the
number of shortfin mako sharks landed
and sold.
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Alternative A4 would establish a
commercial minimum size of 83 inches
FL (210 cm FL) for retention of shortfin
mako sharks caught incidentally during
fishing for other species, whether the
shark is dead or alive at haulback. Based
on observer data, only 8 percent of
shortfin mako sharks are caught with
pelagic longline gear greater than 83
inches FL. Thus, restricting fishermen to
retaining 8 percent of shortfin mako
sharks would represent a considerable
reduction in number of shortfin mako
sharks landed and in the resulting exvessel revenue. A 92 percent reduction
in shortfin mako landings would reduce
annual revenues by an average of $3,802
per vessel for the 88 activate pelagic
longline vessels and would reduce
annual revenues by an average of $858
per vessel for the 10 non-pelagic
longline vessels that land shortfin mako
sharks. However, the overall economic
impacts associated with these
reductions in revenue are not expected
be substantial, as shortfin mako sharks
comprise less than one percent of total
HMS ex-vessel revenues on average.
Additionally, the magnitude of shortfin
mako landings by other gear types (e.g.,
bottom longline, gillnet, handgear) is
very small. Overall, this alternative
would have minor economic impacts on
small entities because these measures
would reduce the number of shortfin
mako sharks landed and sold by these
fishing vessels, however, shortfin mako
sharks are rarely a target species and are
worth less than other more valuable
target species.
Alternative A5 would allow
fishermen to retain shortfin mako sharks
caught on any commercial gear (e.g.,
pelagic longline, bottom longline,
gillnet, handgear) provided that an
observer is on board that can verify that
the shark was dead at haulback. Under
this alternative, electronic monitoring
would not be used to verify the
disposition of shortfin mako sharks
caught on pelagic longline gear, but
instead pelagic longline vessels could
only retain shortfin mako sharks when
the sharks are dead at haulback and an
observer is on board.
Since only five percent of pelagic
longline gear trips are observed, this
alternative would result in a 95 percent
reduction in the number of shortfin
mako sharks retained on pelagic
longline gear. A 95 percent reduction in
shortfin mako landings would reduce
annual revenues by an average of $3,926
per vessel for the 88 activate pelagic
longline vessels and would reduce
annual revenues by an average of $886
per vessel for the 10 non-pelagic
longline vessels that land shortfin mako
sharks. However, the overall economic
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impacts associated with these
reductions in revenue are not expected
be substantial, as shortfin mako sharks
comprise less than one percent of total
HMS ex-vessel revenues on average.
Additionally, the magnitude of shortfin
mako landings by other gear types (e.g.,
bottom longline, gillnet, handgear) is
very small. Overall, this alternative
would have minor economic costs on
small entities because these measures
would reduce the number of shortfin
mako sharks landed and sold by these
fishing vessels, however, shortfin mako
sharks are rarely a target species and are
worth less than other more valuable
target species. Compared to the
preferred Alternative A7, this
alternative would place more restrictive
limits on fishermen using pelagic
longline, bottom longline, and gillnet
gear. Observers are only occasionally on
board vessels, so limiting the retention
of shortfin mako sharks to trips with an
observer would reduce the opportunity
to retain dead individuals. The reduced
opportunity to retain dead shortfin
mako sharks would not reduce fishing
mortality on the stock. Therefore, NMFS
does not prefer this alternative at this
time.
Alternative A6 would place shortfin
mako sharks on the prohibited sharks
list to prohibit any catch or retention of
shortfin mako sharks in commercial
HMS fisheries. In recent years, about
181,000 lb dw of shortfin mako sharks
have been landed and the commercial
revenues from shortfin mako sharks
have averaged approximately $373,000
per year, which equates to
approximately one percent of overall
HMS ex-vessel revenues. That revenue
would be eliminated under this
alternative. Approximately 97.26
percent of shortfin mako commercial
landings, based on dealer reports, were
made by pelagic longline vessels. There
were 88 pelagic longline vessels that
were active in 2017 based on logbook
reports. Therefore, the average loss in
annual revenue from shortfin mako
shark landings per pelagic longline
vessel would be $4,133 per year. The
average loss in annual revenue from
shortfin mako shark landings for vessel
using other gear types would be $933
per year. However, the overall economic
impacts associated with these
reductions in revenue are not expected
be substantial, as shortfin mako sharks
comprise less than one percent of total
HMS ex-vessel revenues on average.
Additionally, the magnitude of shortfin
mako landings by other gear types (e.g.,
bottom longline, gillnet, handgear) is
very small. Overall, this alternative
would have minor economic costs on
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small entities because these measures
would reduce the number of shortfin
mako sharks landed and sold by these
fishing vessels, however, shortfin mako
sharks are rarely a target species and are
worth less than other more valuable
target species. Therefore, NMFS does
not prefer this alternative at this time.
Based on public comment, Alternative
A7 is a new alternative in this FEIS that
is a logical outgrowth of the previouslypreferred Alternative A2. Under
preferred Alternative A7, shortfin mako
sharks caught using gillnet, bottom
longline, or pelagic longline gear on
properly-permitted vessels could be
retained, provided they are dead at
haulback. In the case of pelagic longline
vessels, an electronic monitoring system
would be required, but not on bottom
longline of gillnet vessels.
During the public comment period,
some commenters that expressed
support for the DEIS preferred
alternative also voiced support for
expanding the ability to retain dead
shortfin mako sharks should not be
limited solely to the pelagic longline
gear, and they felt that requiring
electronic monitoring systems on small
vessels essentially would effectively
create such a restriction. Although the
DEIS preferred alternative did not limit
the ability to retain dead shortfin mako
sharks to pelagic longline vessels, the
requirement to install a costly electronic
monitoring system to do so may have
limited the measure to the pelagic
longline fishery. HMS-permitted pelagic
longline vessels are already required to
have electronic monitoring systems on
board, but vessels using other gear types
are unlikely to install the costly system
in order to retain shortfin mako sharks,
especially considering the relatively low
ex-vessel value. Thus, the practical
effect of Alternative A2 could be to limit
the measure to pelagic longline vessels.
To address the public comments, NOAA
Fisheries now prefers Alternative A7, a
newly added alternative in the FEIS that
is a slightly modified extension of
Alternative A2. Under preferred
Alternative A7, shortfin mako sharks
caught using gillnet, bottom longline, or
pelagic longline gear on properlypermitted vessels could be retained,
provided they are dead at haulback. In
the case of pelagic longline vessels, an
electronic monitoring system would be
required, but not on bottom longline or
gillnet vessels.
This alternative would have a similar
impact as Alternative A2 for pelagic
longline vessels (reducing revenues by
an average of $3,058 per vessel), but it
would not impact the estimated 10 nonpelagic longline vessels. Therefore, it
would prevent the estimated $933 in
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5371
reduced landings per vessel for those
non-pelagic longline vessels that would
occur under Alternative A2. Allowing
fishermen to retain dead shortfin mako
sharks caught in bottom longline or
gillnet gear is unlikely to have a large
impact since these gear types rarely
interact with the species. Overall, this
alternative would have minor economic
costs on small entities because these
measures would reduce the number of
shortfin mako sharks landed and sold by
these fishing vessels. However, shortfin
mako sharks are rarely a target species
and are worth less than other more
valuable target species. NMFS prefers
this alternative because it achieves the
objectives of the amendment and largely
the same conservation benefit while
easing costly requirements on small
vessels and thus with less economic
impact or restrictions on commercial
fishermen.
While HMS Angling permit holders
are not considered small entities by
NMFS for purposes of the Regulatory
Flexibility Act, Charter/Headboat permit
holders and tournament operators are
considered to be small entities and
could be potentially impacted by the
various recreational alternatives, as
described below.
NMFS received public comment that
indicated the proposed suite of
measures presented in Alternatives B2
through B8 particularly restricted
vessels with multiple HMS permits.
These vessels generally fish with rod
and reel or other handgear as opposed
to pelagic longline, bottom longline, or
gillnet gear. However, these vessels are
part of the ICCAT fishery as they
regularly target tunas, billfish, and
swordfish. For the sake of clarity, we are
therefore limiting them to the
recreational shark requirements when
shortfin mako sharks are onboard, and
prohibiting them from selling any
sharks when recreationally retaining
shortfin mako sharks.
For these alternatives, a vessel issued
both a Federal Atlantic commercial
shark vessel permit under § 635.4(e) and
an HMS Charter/Headboat permit with
a shark endorsement under § 635.4(b)
could land shortfin mako sharks in
accordance with the recreational size
limits under § 635.20(e), but could not
retain them commercially. This will
limit the ability of a small number of
vessels to generate commercial revenue
from sharks while landing shortfin
mako sharks under the recreational size
limits. In fact, there were only 35
General Category and 14 Charter/
Headboat vessels with Directed or
Incidental Shark permits in 2017.
Between 2012 and 2017, shortfin mako
sharks caught on hook and line or
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handline only composed less than 1
percent of commercial landings. On an
individual vessel basis, a prohibition on
the landing of shortfin mako sharks is
unlikely to affect the profitability of a
commercial charter/headboat trip or the
value of a shark incidental limited
access permit on the open market. Exvessel prices for shortfin mako sharks
are only around $1.50 per pound while
prices for yellowfin, bigeye, and bluefin
tuna can range from $3.50 to $8.00 per
pound (2017 SAFE Report). Thus,
shortfin mako sharks are less valuable
than target tuna species. Furthermore,
other incidentally-caught sharks could
still be legally retained and sold.
Similarly, a vessel issued both a
Federal Atlantic commercial shark
vessel permit under § 635.4(e) and an
Atlantic Tunas General category permit
under § 635.4(d) or a Swordfish General
Commercial permit under § 635.4(f)
with a shark endorsement could land
shortfin mako sharks in accordance with
the recreational size limits under
§ 635.20(e) when fishing in a registered
HMS tournament § 635.4(c)(2). If a
shortfin mako shark is retained by such
vessels, any other shark species being
retained cannot exceed the recreational
retention limits under § 635.22(c) and
cannot be sold.
Alternative B1, the no action
alternative, would not implement any
management measures in the
recreational shark fishery to decrease
mortality of shortfin mako sharks. This
would result in no additional economic
impacts on small entities associated
with this fishery in the short-term.
Under Alternative B2, the preferred
alternative, the minimum size limit for
the retention of shortfin mako sharks
would be increased from 54 inches FL
to 71 inches FL for male and 83 inches
FL for female shortfin mako sharks.
Under the proposed rule and Draft
Amendment 11, Alternative B2 was not
a preferred alternative. Instead, NMFS
had preferred Alternative B3 which
implemented a single size limit of 83
inches FL for all shortfin mako sharks.
NMFS has decided to change that for a
number of reasons including public
comment, greater than estimated
landings reductions under the 83 inch
FL size limit implemented under the
emergency interim rule, evidence of
reduced directed effort for shortfin
mako sharks under the emergency
interim rule, and because this
alternative would not increase harvest
of mature female sharks compared to the
83 inch size limit implemented by the
emergency interim final rule.
NMFS received a number of public
comments urging the agency to adopt
this alternative as the preferred
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alternative, and implement the size
limits specified in one of the measures
of the ICCAT recommendation.
Commenters pointed out that the U.S.
delegation had supported the
recommendation, and that U.S.
recreational landings consisted of less
than 5 percent of total international
landings of shortfin mako sharks. As
such, the added reduction in landings
by implementing the 83 inch FL
minimum size limit for both sexes
would result in a minimal reduction of
total international landings while
greatly impacting the U.S. recreational
fishery. Furthermore, any increases in
shortfin mako landings under
Alternative B2 would consist solely of
male sharks as the minimum size limit
for female sharks would remain the
same.
This increase in the minimum size
limit is projected to reduce recreational
landings by at least 65 percent in
numbers of sharks landed, and 50
percent in the weight of sharks landed.
While this alternative would not
establish a shortfin mako fishing season,
such a significant increase in the
minimum size limit would likely result
in some reduction in directed fishing
effort for shortfin mako sharks. Effort
data collected via the LPS suggests there
has been a significant reduction in
directed fishing trips targeting shortfin
mako sharks compared to the five year
average under the 83 inch size limit
implemented by the emergency interim
final rule. Estimates of directed trips for
shortfin mako sharks declined by 34
percent compared to the six year
average from 2012 through 2017
resulting in greater than projected
reductions in shortfin mako shark
landings. This time period (June
through August) traditionally accounts
for over 90 percent of directed trips for
shortfin mako sharks. Based on the LPS
data from 2012–2017, shortfin mako
sharks were the primary target species
in approximately 67 percent of trips that
caught and 75 percent of trips that
landed them. As such, a reduction in
directed fishing effort could
substantially reduce the landings
expected under this alternative. While
this alternative is unlikely to affect
directed effort as significantly as the 83
inch size limit, NMFS anticipates
directed effort will not fully recover to
previous levels.
Under Alternative B3, the minimum
size limit for retention of shortfin mako
sharks would be increased to 83 inches
FL for both males and female sharks
consistent with the measure
implemented in the emergency rule.
Assuming no reduction in directed
fishing effort, this increase in the
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minimum size limit would result in an
83 percent reduction in the number of
sharks landed, and a 69 percent
reduction in the weight of sharks
landed. Such a large increase in the
minimum size limit and associated
reduction in landings is unlikely to have
no effect on directed fishing effort, in
fact, an approximately 34 percent
reduction in directed effort was
observed in the summer of 2018
following the implementation of this
size limit under the emergency interim
final rule. An 83 percent reduction in
shortfin mako sharks harvested would
thus reduce the percentage of directed
trips harvesting them by about 6
percent. At least three tournaments
directed at shortfin mako sharks in the
Northeast chose to cancel 2018 events
due to the more stringent current 83
inches FL minimum size limit.
Tournaments account for over half of
directed recreational trips for shortfin
mako sharks, and 77 percent of them in
the month of June when effort is at its
highest. This could result in a
substantial reduction in directed fishing
trips for shortfin mako sharks, thus
leading to moderate adverse economic
impacts on some charter/headboats and
tournament operators. NMFS no longer
prefers Alternative B3 at this time as
reduction in directed fishing effort
following implementation of the
emergency interim final rule suggests
this alternative may be more restrictive
than needed to achieve the reductions
targets recommended by ICCAT, and
could place an undue burden on the
recreational fishery.
Under Alternative B4, recreational
HMS permit holders would only be
allowed to retain male shortfin mako
sharks that measure at least 71 inches
FL and female shortfin mako sharks that
measure at least 108 inches FL.
Assuming no reduction in directed
fishing effort, this increase in the
minimum size limit would result in a 77
percent reduction in the number of
sharks landed. A 73 percent reduction
in shortfin mako sharks harvested
would thus reduce the percentage of
directed trips harvesting them to
approximately 9 percent. This could
result in a significant reduction in
directed fishing trips for shortfin mako
sharks, thus leading to moderate adverse
economic impacts on some charter/
headboats and tournament operators.
Under Alternative B5, recreational
HMS permit holders would only be
allowed to retain male shortfin mako
sharks that measure at least 71 inches
FL and female shortfin mako sharks that
measure at least 120 inches FL.
Assuming no reduction in directed
fishing effort, this increase in the size
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limit would result in a 78 percent
reduction in the number of sharks
landed, and a 74 percent reduction in
the weight of sharks landed. A 78
percent reduction in shortfin mako
sharks harvested would thus reduce the
percentage of directed trips harvesting
them to 8.6 percent. This could result in
a significant reduction in directed
fishing trips for shortfin mako sharks,
thus leading to moderate adverse
economic impacts on some charter/
headboats and tournament operators.
Under Alternative B6a, the minimum
size limit for the retention of shortfin
mako sharks would be increased from
54 inches FL to 71 inches FL for male
and 83 inches FL for female shortfin
mako sharks, and a shortfin mako
fishing season would be established
from May through October. The fishing
season established under this alternative
would have little to no effect on shortfin
mako fishing activity in the Northeast,
but may reduce fishing effort in the
South Atlantic and Gulf of Mexico
regions; however, a lack of data on
targeted trips for shortfin mako sharks
in this region makes any assessment of
potential socioeconomic impacts
difficult. However, this combination of
increase in the size limit and fishing
season is projected to reduce
recreational landings by at least 65
percent in numbers of sharks landed,
and 50 percent in the weight of sharks
landed in the Northeast. A 65 percent
reduction in shortfin mako sharks
harvested would thus reduce the
percentage of directed trips harvesting
them to 13 percent. This reduction on
directed trips could lead to moderate
adverse economic impacts on some
charter/headboats and tournament
operators. NMFS does not prefer this
alternative at this time, as it is unlikely
to result in significantly greater
reductions in landings than the
preferred alternative, Alternative B2,
and could potentially result in regional
inequalities in access to the recreational
shortfin mako shark fishery due to
difference in seasonal abundance.
Under Alternative B6b, NMFS would
establish a three-month fishing season
for shortfin mako sharks spanning the
summer months of June through August.
This season would be combined with a
71-inch FL minimum size limit for
males and 100 inch minimum size FL
for females. Based on estimates from the
LPS, on average 475 directed trips are
taken for shortfin mako sharks each
September and October, representing
approximately 9 percent of all annual
directed trips. No registered HMS
tournaments held in September and
October target sharks exclusively, so it
is highly unlikely this alternative would
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result in the rescheduling of any
tournaments due to the fishing season.
It is much more likely that directed
fishing effort would be affected by the
increases in the minimum size limits.
Assuming this increase in the size limit
has minimal effect on fishing effort
directly towards shortfin mako sharks
within the season, this combination of
season and increase in the size limit
should result in a 79 percent reduction
in the number of sharks landed, and a
74 percent reduction in the weight of
sharks landed. This reduction could
result in a significant reduction in
directed fishing trips for shortfin mako
sharks, thus leading to moderate adverse
economic impacts on some charter/
headboat operators. NMFS does not
prefer this alternative at this time as
observed reductions in directed fishing
effort following implementation of the
emergency interim rule suggest this
alternative may be more restrictive than
is needed to meet the 72 to 79 percent
reduction targets recommended by
ICCAT.
Under Alternative B6c, NMFS would
establish a two-month fishing season for
shortfin mako sharks for the months of
June and July. This season would be
combined with a 71-inch FL minimum
size limit for males and 90-inch
minimum sizes FL for females. Based on
estimates from the LPS, on average
1,264 directed trips are taken for
shortfin mako sharks each August
through October, representing
approximately 26 percent of all annual
directed trips. Only two registered HMS
tournaments held in August through
October target sharks exclusively, one
out of New York that primarily targets
thresher sharks and one out of Florida
where participants fish exclusively from
shore. Thus, it is highly unlikely this
alternative would result in the
rescheduling of any tournaments due to
the fishing season. It is likely that
directed fishing effort would also be
affected by the increases in the
minimum size limits. Assuming this
increase in the size limit has minimal
effect on fishing effort directly towards
shortfin mako sharks within the season,
this combination of season and increase
in the size limit should result in a 77
percent reduction in the number of
sharks landed, and a 69 percent
reduction in the weight of sharks
landed. Such a large increase in the size
limit and associated reduction in
landings is unlikely to have no effect on
directed fishing effort. A 77 percent
reduction in shortfin mako sharks
harvested would thus reduce the
percentage of directed trips harvesting
them to 8 percent. This reduction in
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5373
directed trips could lead to moderate
adverse economic impacts on some
charter/headboats and tournament
operators. NMFS does not prefer this
alternative at this time as observed
reductions in directed fishing effort
following implementation of the
emergency interim rule suggest this
alternative may be more restrictive than
is needed to meet the 72 to 79 percent
reduction targets recommended by
ICCAT.
Under Alternative B6d, NMFS would
establish a one-month fishing season for
shortfin mako sharks for the month of
June only. This season would be
combined with a 71 inches FL
minimum size limit for males and 83
inches FL for females. Based on
estimates from the LPS, on average
2,435 directed trips are taken for
shortfin mako sharks each July through
October, representing approximately 52
percent of all annual directed trips.
Additionally, there are seven registered
HMS tournaments held in July through
October that target sharks exclusively,
including three of four tournaments
held in the state of Rhode Island, and
the only tournament in Massachusetts to
target sharks exclusively. It is likely that
directed fishing effort would also be
affected by the increases in the
minimum size limits. Assuming this
increase in the size limit has minimal
effect on fishing effort directly towards
shortfin mako sharks within the season,
this combination of season and increase
in the size limit should result in an 80
percent reduction in the number of
sharks landed, and a 76 percent
reduction in the weight of sharks
landed. Such a large increase in the size
limit and associated reduction in
landings is unlikely to have no effect on
directed fishing effort. An 80 percent
reduction in shortfin mako sharks
harvested would thus reduce the
percentage of directed trips harvesting
them to 8 percent. This reduction in
directed trips could lead to moderate
adverse economic impacts on some
charter/headboats and tournament
operators.
Under Alternative B6e, NMFS would
establish a process and criteria for
determining season dates and minimum
size limits for shortfin mako sharks on
an annual basis through inseason
actions. This process would be similar
to how the agency sets season opens and
retention limits for the shark
commercial fisheries and the Atlantic
Tunas General category fishery. NMFS
would review data on recreational
landings, catch rates, and effort levels
for shortfin mako sharks in the previous
years, and establish season dates and
minimum size limits that would be
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expected to achieve the reduction
targets established by ICCAT, and the
objectives of the HMS fisheries
management plan. This alternative
would also allow NMFS to minimize
adverse economic impacts to the HMS
recreational fishery by allowing for
adjustments to the season and size
limits based on observed reductions and
redistribution of fishing effort resulting
from measures implemented in previous
years. NMFS does not prefer this
alternative at this time as the
establishment of a shortfin mako shark
fishing season has the potential to create
regional inequalities in access to the
fishery given its wide spatial and
temporal nature as a highly migratory
species. These potential inequalities
would appear to be unjustified as there
are alternatives available that are
capable of meeting the reductions
recommended by ICCAT without them.
Under Alternative B7, NMFS would
implement a ‘‘slot limit’’ for shortfin
mako sharks in the recreational fishery.
Under a slot limit, recreational
fishermen would only be allowed to
retain shortfin mako sharks within a
narrow size range (e.g., between 71 and
83 inches FL) with no retention above
or below that slot. Assuming no
reduction in directed fishing effort, this
alternative would be expected to result
in similar reductions in landings as
other alternatives analyzed here. While
this alternative would not establish a
shortfin mako fishing season, as
described above in earlier alternatives,
such a significant increase in the size
limit would likely result in some
reduction in directed fishing effort for
shortfin mako sharks and shifting focus
to other HMS species. This reduction in
effort may be further exacerbated by the
complicated nature of slot limits
regulations. The amount of effort
reduction by recreational fishermen
would depend on how much HMS
anglers and tournaments are satisfied to
practice catch-and-release fishing for
sub-legal shortfin mako sharks or shift
their fishing effort to other species.
NMFS does not prefer this alternative at
this time as there are less complicated
options available that are capable of
meeting the mortality reductions
recommended by ICCAT.
Under Alternative B8, NMFS would
establish a landings tag requirement and
a yearly limit on the number of landings
tags assigned to a vessel, for shortfin
mako sharks over the minimum size
limit. This requirement would be
expected to negatively affect fishing
effort. An increase in the minimum size
limit and a yearly cap on landings for
vessels would reduce effort drastically,
while maintaining some opportunity for
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the recreational fleet. This effort
reduction would adversely affect the
charter fleet the most by limiting the
number of trips on which they could
land shortfin mako sharks each year.
This effort reduction may also affect
their ability to book trips. At least one
tournament directed at shortfin mako
sharks in the Northeast chose to cancel
its 2018 event due to the more stringent
current 83-inch FL minimum size limit.
By excluding tournaments from a
landings tag requirement there may be
a direct beneficial economic impact for
tournaments, as this would be an
additional opportunity, beyond their
tags, to land shortfin mako sharks for
permit holders.
Alternative B9, the preferred
alternative, would expand the
requirement to use non-offset, nonstainless steel circle hook by all HMS
permit holders with a shark
endorsement when fishing for sharks
recreationally, except when fishing with
flies or artificial lures, in federal waters.
Currently, this requirement is in place
for all federally managed waters south
of 41°43′ N latitude (near Chatham,
Massachusetts), but this alternative
would remove the boundary line,
requiring fishermen in all areas to use
circle hooks. Recreational shark
fishermen north of Chatham,
Massachusetts would need to purchase
circle hooks to comply with this
requirement, although the cost is
modest. Additionally, it is possible that
once the circle hook requirement is
expanded, fishermen in the newly
impacted area could find reduced catch
rates of sharks including shortfin mako
sharks. If reduced catch rates are
realized, effort in the recreational shark
fishery, including the for-hire fleet,
could be impacted by reduced number
of trips or reduced demand for chartered
trips.
Alternative B10 would place shortfin
mako sharks on the prohibited sharks
list to prohibit the retention of shortfin
mako sharks in recreational HMS
fisheries. HMS permit holders would be
prohibited from retaining or landing
shortfin mako sharks recreationally. In
recreational fisheries, recreational
fishermen would only be authorized to
catch and release shortfin mako sharks.
A prohibition on the retention of
shortfin mako sharks is likely to
disincentivize some portion of the
recreational shark fishery, particularly
those individuals that plan to target
shortfin mako sharks. Businesses that
rely of recreational shark fishing such as
and tournament operators and charter/
headboats may experience a decline in
demand resulting in adverse economic
impacts. NMFS does not prefer this
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alternative at this time as it would
prohibit all retention of shortfin mako
sharks in the recreational fishery. As
such, Alternative B10 would create
unnecessary inequalities between the
commercial and recreational fishing
sectors when other alternatives are
available that can achieve the ICCAT
recommended landings reduction in a
more equitable fashion.
Alternative C1, the preferred
alternative, would make no changes to
the current reporting requirements
applicable to shortfin mako sharks in
HMS fisheries. Since there would be no
changes to the reporting requirements
under this alternative, NMFS would
expect fishing practices to remain the
same and direct economic impacts in
small entities to be neutral in the shortterm.
Under Alternative C2, NMFS would
require vessels with a directed or
incidental shark LAP to report daily the
number of shortfin mako sharks retained
and discarded dead, as well as fishing
effort (number of sets and number of
hooks) on a VMS. A requirement to
report shortfin mako shark catches on
VMS for vessels with a shark LAP
would be an additional reporting
requirement for those vessels on their
existing systems. For other commercial
vessels that are currently only required
to report in the HMS logbook, the
requirement would mean installing
VMS to report dead discards of shortfin
mako and fishing effort.
If a vessel has already installed a typeapproved E–MTU VMS unit, the only
expense would be monthly
communication service fees, which it
may already be paying if the vessel is
participating in a Council-managed
fishery. Existing regulations require all
vessel operators with E–MTU VMS
units to provide hail out/in declarations
and provide location reports on an
hourly basis at all times while they are
away from port. In order to comply with
these regulations, vessel owners must
subscribe to a communication service
plan that includes an allowance for
sending similar declarations (hail out/
in) describing target species, fishing gear
possessed, and estimated time/location
of landing using their E–MTU VMS.
Given that most shortfin mako sharks
are incidentally caught by pelagic
longline vessels that are already
required to have an E–MTU VMS
system onboard, adverse economic
impacts are not expected. If vessels with
a shark LAP do not have an E–MTU
VMS unit, direct, economic costs are
expected as a result of having to pay for
the E–MTU VMS unit (approximately
$4,000) and a qualified marine
electrician to install the unit ($400).
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VMS reporting requirements under this
alternative could potentially provide
undue burden to HMS commercial
vessels that already report on catches,
landings, and discards through vessel
logbooks, dealer reports, and observer
reports.
Alternative C3 would implement
mandatory reporting of all recreational
interactions (landed and discarded) of
shortfin mako sharks in HMS fisheries.
Recreational HMS permit holders would
have a variety of options for reporting
shortfin mako shark landings including
a phone-in system, internet website,
and/or a smartphone app. HMS Angling
and Charter/Headboat permit holders
currently use this method for required
reporting of each individual landing of
bluefin tuna, billfish, and swordfish
within 24 hours. NMFS has also
maintained a shortfin mako shark
reporting app as an educational tool to
encourage the practice of catch-andrelease. Additionally, the potential
burden associated with mandatory
landings reports for shortfin mako
sharks would be significantly reduced
under the increased minimum size
limits being considered in this
rulemaking, although would still
represent an increased burden over
current reporting requirements. While
HMS Angling permit holders are not
considered small entities by NMFS for
purposes of the Regulatory Flexibility
Act, Charter/Headboat permit holders
are considered to be small entities and
would be potentially impacted by this
alternative.
Under Alternative D1, NMFS would
not establish a rebuilding plan or the
foundation for rebuilding the shortfin
mako shark stock. NMFS would still
implement management measures in the
HMS recreational and commercial
fisheries to end overfishing consistent
with the Magnuson-Stevens Act and
with ICCAT Recommendation 17–08
and our obligations under ATCA. There
would likely be no direct short-term
impact on small entities from this
alternative as there would be no change
in fishing effort or landings of shortfin
mako sharks that would impact
revenues generated from the commercial
and recreational fisheries.
Under Alternative D2, NMFS would
establish a domestic rebuilding plan
independent of a rebuilding plan
adopted by ICCAT. While such an
alternative could avoid overfishing
shortfin mako sharks in the United
States by changing the way that the U.S.
recreational and commercial fisheries
operate, such a plan could not
effectively rebuild the stock, since U.S.
catches are only 9 percent of the
reported catch Atlantic-wide. Such an
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alternative would be expected to cause
short- and long-term direct economic
impacts.
Under Alternative D3, the preferred
alternative, NMFS would take
preliminary action toward rebuilding by
adopting measures to end overfishing to
establish the foundation for a rebuilding
plan. NMFS would then take action at
the international level through ICCAT to
develop a rebuilding plan for shortfin
mako sharks. ICCAT may establish a
rebuilding plan for shortfin mako sharks
in 2019, and this rebuilding plan would
encompass the objectives set forth by
ICCAT based on scientific advice from
the SCRS. This alternative would not
result in any changes to the current
recreational and commercial domestic
regulations for shortfin mako sharks in
the short-term. There would likely be no
direct short-term impact on small
entities from this alternative as there
would be no change in fishing effort or
landings of shortfin mako sharks that
would impact revenues generated from
the commercial and recreational
fisheries. Management measures to
address overfishing of shortfin mako
sharks could be adopted in the future.
These measures could change the way
that the U.S. recreational and
commercial shortfin mako shark fishery
operates, which could cause long-term
direct economic impacts. Any future
action to implement international
measures would be analyzed in a
separate rulemaking.
Under Alternative D4, NMFS would
remove shortfin mako sharks from the
commercial pelagic shark management
group and would implement a speciesspecific quota for shortfin mako sharks
as established by ICCAT. A shortfin
mako-specific quota would likely
include both commercial and
recreational catches, as do other ICCAT
established quotas. In addition, NMFS
would establish a new commercial
pelagic shark species quota for common
thresher and oceanic whitetip sharks
based on recent landings. The 2017
ICCAT stock assessment indicated that
the North Atlantic population of
shortfin mako sharks is overfished and
experiencing overfishing. In November
2017, ICCAT adopted management
measures (Recommendation 17–08) to
address the overfishing determination,
but did not recommend a TAC
necessary to stop overfishing of shortfin
mako sharks. Therefore, it is difficult at
this time to determine how setting a
species-specific quota for shortfin mako
sharks would affect commercial and
recreational fishing operations.
However, this species-specific quota
may provide long-term direct, minor
adverse economic impacts if ICCAT
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5375
established a TAC for the United States
that is well below the total average
harvest by the United States (i.e., 330 mt
ww or 168 mt dw) or below the current
annual commercial quota for common
thresher, oceanic whitetip, and shortfin
mako (488 mt dw) as it could potentially
limit the amount of harvest for
fishermen. Short-term direct
socioeconomic impacts would be
neutral for Alternative D4 because
initially there would be no reduction in
fishing effort and practices.
Under Alternative D5, NMFS would
take steps to implement area-based
management measures domestically if
such measures are established by
ICCAT. ICCAT Recommendation 17–08
calls on the SCRS to provide additional
scientific advice in 2019 that takes into
account a spatial/temporal analysis of
North Atlantic shortfin mako shark
catches in order to identify areas with
high interactions. Without a specific
area to analyze at this time, the precise
impacts on commercial and recreational
fishery operations cannot be
determined. Implementing area
management for shortfin mako sharks, if
recommended by the scientific advice,
could lead to a reduction in localized
fishing effort, which would likely have
adverse economic impacts for small
entities that land shortfin mako sharks.
Under Alternative D6, NMFS would
annually allocate a specific number of
‘‘allowable’’ dead discards of shortfin
mako sharks as a bycatch cap or subannual catch limit (ACL) that would
apply to all fisheries, not just HMS
fisheries. This alternative would impact
the HMS pelagic longline and shark
recreational fisheries similar to
Alternative D4. However, this
alternative could also impact non-HMS
fisheries by closing those fisheries if the
bycatch cap were reached. This
alternative could lead to short-term
adverse impacts since the bycatch caps
could close fisheries if they are reached
until those fishermen could modify
fishing behavior to avoid shortfin mako
sharks (even in fisheries where shortfin
mako sharks are rarely, if ever, seen)
and reduce interactions. In the longterm, this alternative would have
neutral impacts as the vessels would
avoid shortfin mako sharks. The impacts
to small businesses are expected to be
neutral in the short and long-term as
their businesses would not change.
Section 212 of the Small Business
Regulatory Enforcement Fairness Act of
1996 states that, for each rule or group
of related rules for which an agency is
required to prepare a FRFA, the agency
shall publish one or more guides to
assist small entities in complying with
the rule, and shall designate such
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publications as ‘‘small entity
compliance guides.’’ The agency shall
explain the actions a small entity is
required to take to comply with a rule
or group of rules. As part of this
rulemaking process, NMFS has prepared
a listserv summarizing fishery
information and regulations for Atlantic
shark fisheries for 2019. This listserv
also serves as the small entity
compliance guide. Copies of the
compliance guide are available from
NMFS (see ADDRESSES).
NMFS prepared a FEIS for this final
rule that discusses the impact on the
environment that would result from this
rule. A copy of the FEIS is available
from NMFS (see ADDRESSES).
(6) For North Atlantic shortfin mako
sharks landed under the recreational
retention limits specified at
§ 635.22(c)(2), males must be at least 71
inches (180 cm) fork length, and females
must be at least 83 inches (210 cm) fork
length.
*
*
*
*
*
■ 4. Amend § 635.21 by:
■ a. Adding paragraphs (a)(4), (c)(1)(iv),
and (d)(5);
■ b. Revising paragraphs (f)(2) and (3);
■ c. Adding paragraph (g)(6); and
■ d. Revising (k)(1) and (2).
The additions and revisions read as
follows:
List of Subjects in 50 CFR Part 635
(a) * * *
(4) Any person on board a vessel that
is issued a commercial shark permit
must release all shortfin mako sharks,
whether alive or dead, caught with any
gear other than pelagic longline, bottom
longline, or gillnet gear, except that any
person on board a vessel that is issued
a commercial shark permit in
combination with a permit that has a
shark endorsement may retain shortfin
mako sharks subject to the recreational
minimum size limits in § 635.20, the
recreational retention limits in § 635.22,
and authorized gear requirements in
§ 635.19.
*
*
*
*
*
(c) * * *
(1) * * *
(iv) Has pelagic longline gear on
board, persons aboard that vessel are
required to promptly release in a
manner that causes the least harm any
shortfin mako shark that is alive at the
time of haulback. Any shortfin mako
shark that is dead at the time of
haulback may be retained provided the
electronic monitoring system is
installed and functioning in compliance
with the requirements at § 635.9.
*
*
*
*
*
(d) * * *
(5) If a vessel issued or required to be
issued a permit under this part has
bottom longline gear on board persons
aboard that vessel are required to
promptly release in a manner that
causes the least harm, any shortfin mako
shark that is alive at the time of
haulback.
*
*
*
*
*
(f) * * *
(2) A person on board a vessel that
has been issued or is required to be
issued a permit with a shark
endorsement under this part and who is
participating in an HMS registered
tournament that bestows points, prizes,
or awards for Atlantic sharks must
Fisheries, Fishing, Fishing vessels,
Foreign relations, Imports, Penalties,
Reporting and recordkeeping
requirements, Treaties.
Dated: February 15, 2019.
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 635 is amended
as follows:
PART 635—ATLANTIC HIGHLY
MIGRATORY SPECIES
1. The authority citation for part 635
continues to read as follows:
■
Authority: 16 U.S.C. 971 et seq.; 16 U.S.C.
1801 et seq.
2. In § 635.2, revise definition of ‘‘FL
(fork length)’’ to read as follows:
■
§ 635.2
Definitions.
*
*
*
*
*
FL (fork length) means the straightline measurement of a fish from the
midpoint of the anterior edge of the fish
to the fork of the caudal fin. The
measurement is not made along the
curve of the body.
*
*
*
*
*
■ 3. In § 635.20, lift the suspension on
paragraph (e)(2) and revising it and by
adding paragraph (e)(6) to read as
follows:
§ 635.20
Size limits.
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*
*
*
*
*
(e) * * *
(2) All sharks, except as otherwise
specified in paragraphs (e)(3) through
(6) of this section, landed under the
recreational retention limits specified at
§ 635.22(c)(2) must be at least 54 inches
(137 cm) FL.
*
*
*
*
*
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§ 635.21 Gear operation and deployment
restrictions.
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deploy only non-offset, corrodible circle
hooks when fishing for, retaining,
possessing, or landing sharks, except
when fishing with flies or artificial
lures.
(3) A person on board a vessel that
has been issued or is required to be
issued an HMS Angling permit with a
shark endorsement or an HMS Charter/
Headboat permit with a shark
endorsement must deploy only nonoffset, corrodible circle hooks when
fishing for, retaining, possessing, or
landing sharks, except when fishing
with flies or artificial lures.
*
*
*
*
*
(g) * * *
(6) If a vessel issued or required to be
issued a permit under this part has
gillnet gear onboard, persons aboard
that vessel are required to promptly
release in a manner that causes the least
harm any shortfin mako shark that is
alive at the time of haulback.
*
*
*
*
*
(k) * * *
(1) A person on board a vessel that
has been issued or is required to be
issued a permit with a shark
endorsement under this part and who is
participating in an HMS registered
tournament that bestows points, prizes,
or awards for Atlantic sharks must
deploy only non-offset, corrodible circle
hooks when fishing for, retaining,
possessing, or landing sharks, except
when fishing with flies or artificial
lures.
(2) A person on board a vessel that
has been issued or is required to be
issued an HMS Angling permit with a
shark endorsement or a person on board
a vessel with an HMS Charter/Headboat
permit with a shark endorsement must
deploy only non-offset, corrodible circle
hooks when fishing for, retaining,
possessing, or landing, except when
fishing with flies or artificial lures.
*
*
*
*
*
■ 5. In § 635.22, revise paragraph (c)(1)
and add paragraph (c)(7) as follows:
§ 635.22
Recreational Retention Limits.
(c) * * *
(1) The recreational retention limit for
sharks applies to any person who fishes
in any manner on a vessel that has been
issued or is required to have been issued
a permit with a shark endorsement,
except as noted in paragraph (c)(7) of
this section. The retention limit can
change depending on the species being
caught and the size limit under which
they are being caught as specified under
§ 635.20(e). A person on board a vessel
that has been issued or is required to be
issued a permit with a shark
endorsement under § 635.4 is required
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to use non-offset, corrodible circle
hooks as specified in § 635.21(f) and (k)
in order to retain sharks per the
retention limits specified in this section.
*
*
*
*
*
(7) For persons on board vessels
issued both a commercial shark permit
and a permit with a shark endorsement,
the recreational retention limit and sale
prohibition applies for shortfin mako
sharks at all times, even when the
commercial pelagic shark quota is open.
If such vessels retain a shortfin mako
shark under the recreational retention
limit, all other sharks retained by such
vessels may only be retained under the
applicable recreational retention limits
and may not be sold. If a commercial
Atlantic shark quota is closed under
§ 635.28(b), the recreational retention
limit for sharks and no sale provision in
paragraph (a) of this section will be
applied to persons aboard a vessel
issued a Federal Atlantic commercial
shark vessel permit under § 635.4(e), if
that vessel has also been issued a permit
with a shark endorsement under
§ 635.4(b) and is engaged in a for-hire
fishing trip or is participating in a
registered HMS tournament per
§ 635.4(c)(2).
*
*
*
*
*
■ 6. In § 635.24, lift the suspension on
paragraphs (a)(4)(i) and (iii), and revise
them to read as follows:
§ 635.24 Commercial retention limits for
sharks, swordfish, and BAYS tunas.
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*
*
*
*
*
(a) * * *
(4) * * *
(i) Except as provided in
§ 635.22(c)(7), a person who owns or
operates a vessel that has been issued a
directed shark LAP may retain, possess,
land, or sell pelagic sharks if the pelagic
shark fishery is open per §§ 635.27 and
635.28. Shortfin mako sharks may be
retained by persons aboard vessels using
pelagic longline, bottom longline, or
gillnet gear only if the shark is dead at
the time of haulback and consistent
with the provisions of § 635.21(c)(1),
(d)(5), and (g)(6) and 635.22(c)(7).
*
*
*
*
*
(iii) Consistent with paragraph
(a)(4)(ii) of this section, a person who
owns or operates a vessel that has been
issued an incidental shark LAP may
retain, possess, land, or sell no more
than 16 SCS and pelagic sharks,
combined, per vessel per trip, if the
respective fishery is open per §§ 635.27
and 635.28. Of those 16 SCS and pelagic
sharks per vessel per trip, no more than
8 shall be blacknose sharks. Shortfin
mako sharks may only be retained under
the commercial retention limits by
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persons using pelagic longline, bottom
longline, or gillnet gear, only if the
shark is dead at the time of haulback
and consistent with the provisions at
§ 635.21(c)(1), (d)(5), and (g)(6). If the
vessel has also been issued a permit
with a shark endorsement and retains a
shortfin mako shark, recreational
retention limits apply to all sharks
retained and none may be sold, per
§ 635.22(c)(7).
*
*
*
*
*
7. In § 635.30, paragraph (c)(4) is
revised to read as follows:
*
*
*
*
*
(c) * * *
(4) Persons aboard a vessel that has
been issued or is required to be issued
a permit with a shark endorsement must
maintain a shark intact through landing
and offloading with the head, tail, and
all fins naturally attached. The shark
may be bled and the viscera may be
removed.
*
*
*
*
*
■
8. In § 635.71, revise paragraphs
(d)(22), (23), (27), (28), and (29) to read
as follows:
■
§ 635.71
Prohibitions.
*
*
*
*
*
(d) * * *
(22) Except when fishing only with
flies or artificial lures, fish for, retain,
possess, or land sharks without
deploying non-offset, corrodible circle
hooks when fishing at a registered
recreational HMS fishing tournament
that has awards or prizes for sharks, as
specified in § 635.21(f) and (k).
(23) Except when fishing only with
flies or artificial lures, fish for, retain,
possess, or land sharks without
deploying non-offset, corrodible circle
hooks when issued an Atlantic HMS
Angling permit or HMS Charter/
Headboat permit with a shark
endorsement, as specified in § 635.21(f)
and (k).
*
*
*
*
*
(27) Retain, land, or possess a shortfin
mako shark that was caught with gear
other than pelagic longline, bottom
longline, or gillnet gear as specified at
§ 635.21(a).
(28) Retain, land, or possess a shortfin
mako shark that was caught with pelagic
longline, bottom longline, or gillnet gear
and was alive at haulback as specified
at § 635.21(c)(1), (d)(5), and (g)(6).
(29) As specified at § 635.21(c)(1),
retain, land, or possess a shortfin mako
shark that was caught with pelagic
longline gear when the electronic
monitoring system was not installed and
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5377
functioning in compliance with the
requirements at § 635.9.
*
*
*
*
*
[FR Doc. 2019–02946 Filed 2–20–19; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 170828822–70999–04]
RIN 0648–XG796
Fisheries of the Northeastern United
States; Summer Flounder Fishery;
Quota Transfer
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Temporary rule; quota transfer.
AGENCY:
NMFS announces that the
State of North Carolina is transferring a
portion of its 2019 commercial summer
flounder quota to the State of New
Jersey. This quota adjustment is
necessary to comply with the Summer
Flounder, Scup, and Black Sea Bass
Fishery Management Plan quota transfer
provisions. This announcement informs
the public of the revised commercial
quotas for North Carolina and New
Jersey.
DATES: Effective February 20, 2019,
through December 31, 2019.
FOR FURTHER INFORMATION CONTACT:
Cynthia Ferrio, Fishery Management
Specialist, (978) 281–9180.
SUPPLEMENTARY INFORMATION:
Regulations governing the summer
flounder fishery are found in 50 CFR
648.100 through 648.110. These
regulations require annual specification
of a commercial quota that is
apportioned among the coastal states
from Maine through North Carolina. The
process to set the annual commercial
quota and the percent allocated to each
state is described in § 648.102, and the
initial 2019 allocations were published
on December 17, 2018 (83 FR 64482).
The final rule implementing
Amendment 5 to the Summer Flounder
Fishery Management Plan, as published
in the Federal Register on December 17,
1993 (58 FR 65936), provided a
mechanism for transferring summer
flounder commercial quota from one
state to another. Two or more states,
under mutual agreement and with the
concurrence of the NMFS Greater
Atlantic Regional Administrator, can
transfer or combine summer flounder
SUMMARY:
E:\FR\FM\21FER1.SGM
21FER1
Agencies
[Federal Register Volume 84, Number 35 (Thursday, February 21, 2019)]
[Rules and Regulations]
[Pages 5358-5377]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-02946]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 635
[Docket No. 180212159-9102-02]
RIN 0648-BH75
Atlantic Highly Migratory Species; Shortfin Mako Shark Management
Measures; Final Amendment 11
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS is amending the 2006 Consolidated Atlantic Highly
Migratory Species (HMS) Fishery Management Plan (FMP) based on the
results of the 2017 stock assessment and a subsequent binding
recommendation by the International Commission for the Conservation of
Atlantic Tunas (ICCAT) for North Atlantic shortfin mako sharks. The
North Atlantic shortfin mako shark stock is overfished and is
experiencing overfishing. Consistent with the Magnuson-Stevens Fishery
Conservation and Management Act (Magnuson-Stevens Act) and the Atlantic
Tunas Convention Act (ATCA), NMFS is implementing management measures
that will reduce fishing mortality on shortfin mako sharks and
establish the foundation for rebuilding the shortfin mako shark
population consistent with legal requirements. The final measures could
affect U.S. commercial and recreational fishermen who target and
harvest shortfin mako sharks in the Atlantic Ocean, including the Gulf
of Mexico and Caribbean Sea, by increasing live releases and reducing
landings. NMFS is also clarifying the definition of fork length (FL) in
the definitions section of the HMS regulations.
DATES: This final rule is effective on March 3, 2019.
ADDRESSES: Copies of the Final Amendment 11 to the 2006 Consolidated
HMS FMP, including the Final Environmental Impact Statement (FEIS)
containing a list of references used in this document, the dusky shark
stock assessments, and other documents relevant to this rule are
available from the HMS Management Division website at https://www.fisheries.noaa.gov/topic/atlantic-highly-migratory-species.
FOR FURTHER INFORMATION CONTACT: Gu[yacute] DuBeck or Karyl Brewster-
Geisz at (301) 427-8503.
SUPPLEMENTARY INFORMATION:
Background
The North Atlantic shortfin mako stock is managed primarily under
the authority of the Magnuson-Stevens Act and also under ATCA. The 2006
Consolidated HMS FMP and its amendments are implemented by regulations
at 50 CFR part 635. A brief summary of the background of this final
rule is provided below. Additional information regarding Atlantic shark
management can be found in the FEIS accompanying this final rule for
Amendment 11, the 2006 Consolidated HMS FMP and its amendments, the
annual HMS Stock Assessment and Fishery Evaluation (SAFE) Reports, and
online at https://www.fisheries.noaa.gov/topic/atlantic-highly-migratory-species.
The North Atlantic shortfin mako shark (Isurus oxyrinchus) is a
highly migratory species that ranges across the entire North Atlantic
Ocean and is caught by numerous countries. The stock is predominantly
caught offshore in association with fisheries that primarily target
tunas and tuna-like species. While these sharks are a valued component
of U.S. recreational and commercial fisheries, U.S. catch represents
only approximately 9 percent of the species' total catch in the North
Atlantic by all reporting countries. International measures are,
therefore, critical to the species' effective conservation and
management.
Based on a 2017 ICCAT assessment, on December 13, 2017, NMFS issued
a status determination finding the stock to be overfished and
experiencing overfishing, applying domestic criteria. The 2017
assessment estimated that total North Atlantic shortfin mako catches
across all ICCAT parties are currently between 3,600 and 4,750 metric
tons (mt) per year. The assessment further indicated that such total
catches would have to be at or below 1,000 mt (72-79 percent
reductions) to prevent further population declines, and total catches
of 500 mt or less would be expected to stop overfishing and begin
rebuilding the stock.
Based on this information and given that the stock is primarily
caught in association with ICCAT fisheries, ICCAT at its November 2017
meeting
[[Page 5359]]
adopted management measures for Atlantic shortfin mako in
Recommendation 17-08. The measures largely focused on maximizing live
releases of Atlantic shortfin mako sharks, allowing retention only in
certain limited circumstances, increasing minimum size limits for
retention, and improving data collection in ICCAT fisheries. ICCAT
stated that the measures in the Recommendation were ``expected to
prevent the population from decreasing further, stop overfishing and
begin to rebuild the stock.''
On March 2, 2018, NMFS implemented an interim final rule using
emergency authority under the Magnuson-Stevens Act, 16 U.S.C. 1855(c),
to quickly implement measures in the HMS recreational and commercial
fisheries consistent with Recommendation 17-08. The emergency measures
were initially effective for 180 days, and on August 22, 2018, they
were extended to March 3, 2019 (83 FR 42452). This final rule is
intended to replace these emergency measures with long-term measures.
A Notice of Intent (NOI) to prepare an EIS for Amendment 11 of the
Consolidated HMS FMP was published in the Federal Register on March 5,
2018 (83 FR 9255) and provided notice of the availability of an Issues
and Options document for scoping. Based on the alternatives presented
and commented on during scoping, NMFS published a proposed rule for
Draft Amendment 11 on July 27, 2018 (83 FR 35590), and the
Environmental Protection Agency (EPA) published the notice of
availability of the Draft Environmental Impact Statement (DEIS) on July
27, 2018 (83 FR 35637). The details of this rulemaking can be found in
the proposed rule and are not repeated here.
During the comment period on the proposed rule and DEIS, which
lasted for 73 days, NMFS conducted six public hearings (Texas, Florida,
North Carolina, New Jersey, and Massachusetts) and a public webinar. In
addition, NMFS presented Draft Amendment 11 to the Atlantic HMS
Advisory Panel, four Atlantic Regional Fishery Management Councils (the
New England, Mid-Atlantic, South Atlantic, and the Gulf of Mexico
Fishery Management Councils), and the Atlantic States Marine Fisheries
Commission. The comment period ended on October 8, 2018. The comments
received on Draft Amendment 11 and its proposed rule, and responses to
those comments, are summarized below in the section labeled ``Response
to Comments.''
This final rule implements the measures preferred and analyzed in
the FEIS for Amendment 11 to the 2006 Consolidated HMS FMP in order to
address and establish a foundation for rebuilding the North Atlantic
shortfin mako shark stock, which ICCAT will adopt in 2019 after
obtaining additional scientific information, as set out in
Recommendation 17-08. It also includes a clarification to the
regulatory definition of ``FL (fork length),'' as proposed and
discussed in the DEIS and FEIS. The FEIS analyzed the direct, indirect,
and cumulative impacts on the human environment as a result of the
preferred management measures. The FEIS, including the preferred
management measures, was made available on December 21, 2018 (83 FR
65670). On February 15, 2019, the Assistant Administrator for NOAA
signed a Record of Decision (ROD) adopting these measures as Final
Amendment 11 to the 2006 Consolidated HMS FMP. A copy of the FEIS,
including Final Amendment 11 to the 2006 Consolidated HMS FMP, is
available from the HMS Management Division (see ADDRESSES). In the
FEIS, NMFS divided the alternatives into the following four broad
categories for organizational clarity and to facilitate effective
review: Commercial fishery, recreational fishery, monitoring, and
rebuilding. NMFS fully considered 29 alternatives within these
categories and is implementing five measures, one in the commercial
fishery, two in the recreational fishery (each regarding a different
regulation type), one regarding monitoring, and one regarding
rebuilding the stock, to meet the objectives of the rule and achieve at
least a 75 percent reduction in U.S. shortfin mako shark landings
consistent with the suggested level of reduction recommended in the
stock assessment. The stock assessment recommends this level of
reduction throughout the stock's range, and all ICCAT parties fishing
on the stock are committed to take the specified measures to achieve
the needed reductions. NMFS' detailed analyses of the alternatives are
provided in the FEIS for Draft Amendment 11 (see ADDRESSES for how to
get a copy of the FEIS) and a summary is provided in the FRFA below.
In developing the final measures, NMFS considered the commercial
retention restrictions and the 83-inch FL recreational minimum size
limit temporarily put in place through the emergency interim final
rule, public comments received on that rule, other conservation and
management measures that have been implemented in the HMS fisheries
since 2008 that have affected shark fisheries or shark bycatch in other
fisheries, and public comments received on the proposed rule and DEIS,
including comments provided at the September 2018 HMS Advisory Panel
meeting. In response to public comment on the proposed rule and the
DEIS, NMFS made three changes from the proposed rule in the final rule.
The first change adopts a new commercial measure that is a modified
version of the previously preferred measure. A second change adopts a
different recreational size limit measure that was not preferred in the
proposed rule. A third change clarifies the application of retention
restrictions for the few permit holders who hold a commercial shark
permit and a permit that also allows recreational landings of sharks.
All other proposed conservation measures, as well as the proposed
clarification of the definition of ``fork length,'' did not change
between the proposed and final rules. Measures that are different from
the proposed rule, or measures that were proposed but not implemented,
are described in detail in the section titles, ``Changes from the
Proposed Rule.''
Response to Comments
NMFS received a total of 30 individual written comments on the
proposed rule from fishermen, dealers, and other interested parties
along with State of North Carolina, Commonwealth of Massachusetts, the
Mid-Atlantic and New England Fishery Management Councils, several shark
conservation or other environmental groups, including Oceana, and
several commercial and recreational groups. Oral comments were received
from the South Atlantic Fishery Management Council. All written
comments can be found at https://www.regulations.gov/ by searching for
RIN 0648-BH75. All of the comments received are summarized below.
Comment 1: NMFS received multiple comments expressing support for
Amendment 11 management measures as well as comments opposing
implementation of ICCAT shortfin mako shark recommendations. Commenters
in support of Amendment 11 wanted management measures to prevent
overfishing of shortfin mako sharks by placing limits and restrictions
on fishing that results in mortality of shortfin mako sharks. They also
stressed the need for international cooperation if shortfin mako shark
measures are to be effective and the need for all countries fishing on
the stock to implement comparable regulations as required by ICCAT. In
addition, some commenters cited the importance of shortfin mako sharks
to
[[Page 5360]]
the health of ocean ecosystems. One commenter opposed any management
measures for shortfin mako sharks, citing their understanding of
previous ICCAT stock assessment issues, including the underlying
uncertainties with other shark stock assessments such as the porbeagle
shark assessment. Specifically, this commenter stated that ICCAT had
recommended similar regulations for porbeagle sharks after a stock
assessment, and later changed the results after the United States
supplied additional information.
Response: NMFS agrees that shortfin mako sharks play an important
role in maintaining ocean ecosystems, and notes that there are
statutory obligations to effectively manage shark fisheries, prevent
overfishing, and achieve long-term sustainability of the stock. NMFS
has determined that the management measures in this rule will address
overfishing and begin the process of rebuilding the North Atlantic
shortfin mako shark stock as required by law, understanding that any
effective rebuilding plan or measures to end overfishing depend on
effective international measures, given that the United States
contributes to only a portion of the fishing mortality on the stock.
NMFS believes that the 2017 ICCAT stock assessment for shortfin
mako sharks is not appropriately compared to the previous stock
assessment for porbeagle sharks and generally does not agree with the
commenter's implication that the ICCAT assessments are routinely
flawed. The 2017 ICCAT stock assessment for shortfin mako sharks
included many improvements in the data and modeling compared to
previous shark stock assessments, including past porbeagle and shortfin
mako shark assessments. NMFS has determined that the 2017 SCRS shortfin
mako shark stock assessment is the best scientific information
available for shortfin mako sharks, and NMFS is using the results, as
appropriate, as required under National Standard 2 of the Magnuson-
Stevens Act.
Comment 2: NMFS received comments about the stock assessment
methodology and results. A commenter had concerns that the methodology
applied in evaluating the results of different stock assessment models
used in the 2017 shortfin mako stock assessment introduced an
inappropriate negative bias in the overall assessment results. Other
commenters were concerned about the large change in stock status
between all the most recent previous ICCAT stock assessment results,
the conversion rates used to convert dressed weight to whole weight of
sharks, the potential for under-reporting of harvest by other ICCAT
members particularly those countries that have larger fishing fleets
than the United States, and the potential implications of the Marine
Recreational Information Program (MRIP) catch estimates. These
commenters requested that NMFS postpone implementing Amendment 11 until
the next shortfin mako shark stock assessment is completed.
Response: While there is always uncertainty in stock assessment
data inputs, model outputs, and the subsequent interpretation of
results, the SCRS methodologies appropriately considered how to best
address such uncertainties in this particular context. The SCRS
described these sources of uncertainty and concluded that the 2017
stock assessment was an improvement over previous assessments for
shortfin mako sharks, and reflects the best scientific information
available on the status of the stock. ICCAT reviewed and accepted the
results for use in management, and made specific recommendations which
the United States is obligated to implement as necessary and
appropriate under ATCA. NMFS is also required to take action to end
overfishing and rebuild the stock under the Magnuson-Stevens Act given
the stock's status as overfished with overfishing occurring. If future
stock assessments reach different conclusions regarding shortfin mako
shark stock status, and changes to management measures are recommended
by ICCAT, or if NMFS determines that different measures are needed to
address management of the stock, then such changes may be considered at
that time.
Regarding the comment expressing concern that the United States
used incorrect conversion rates for dressed weight to whole weight of
sharks, this issue has also come up in the context of reporting to
ICCAT. As discussed with the ICCAT Advisory Committee at its Fall
meeting, the United States surveyed other countries regarding the
conversion rates and the manner in which those countries dress their
sharks and then reviewed the data it submitted to ICCAT. Based on this
review of the data and the survey of other countries' conversion
factors, the United States found errors in the shortfin mako shark
commercial landings data previously submitted to ICCAT and determined
that changing the conversion rate to match that used by Spain and
Canada was appropriate. Accordingly, the United States submitted
revised estimates to ICCAT of U.S. harvest for all years. NMFS has
accordingly updated all the numbers from the DEIS in the FEIS to
reflect the updated analyses, since the numbers in the DEIS were based
on the ICCAT submissions. As a result of these revised estimates, the
U.S. proportion of shortfin mako catches compared to all catches by all
countries was reduced from 11 percent to 9 percent. For U.S. harvest,
these changes also resulted in a recalculation of the relative
contribution of commercial and recreational fisheries to domestic
shortfin mako shark mortality. The proportion of recreational to
commercial harvest is not equally split with recreational harvest
accounting for 58 percent and commercial harvest (including landings
and dead discards) accounting for 42 percent.
Comment 3: NMFS received comments regarding the timing and process
of this rulemaking. Commenters urged NMFS to implement management
measures immediately based on the best available science to rebuild the
stock and end overfishing. Other commenters are concerned that this
rulemaking is premature since ICCAT could make changes in upcoming
meetings. Some commenters felt the United States should not act
unilaterally, and implement a rebuilding plan without ICCAT. Another
commenter stated that NMFS has two years to implement rebuilding plans
and management measures once the stock is determined to be overfished
and requested that NMFS wait to implement Amendment 11.
Response: Amendment 11 is responsive to ICCAT Recommendation 17-08,
which is a binding recommendation under the ICCAT Convention, and the
United States is obligated to implement it through regulations as
necessary and appropriate under ATCA. Due to the requirements in
Recommendation 17-08 and the status of shortfin mako sharks, NMFS
worked to immediately implement the requirements in Recommendation 17-
08 via an emergency interim final rule (83 FR 8946; March 2, 2018).
Under sections 305(c) and 304(e)(6) of the Magnuson-Stevens Act, NMFS
has the authority to implement interim measures to reduce overfishing
on an emergency basis for 180 days. Those measures can be extended
again for another 186 days if necessary. NMFS later extended the
emergency rule for another 186 days; these emergency measures expire on
March 3, 2019 (83 FR 42452; August 22, 2018). NMFS aims to have the
management measures in Amendment 11 in place by the time the emergency
rule expires or soon thereafter. If ICCAT changes the measures in
Recommendation 17-08 at future meetings, then the United States will be
[[Page 5361]]
responsive to those changes, consistent with ATCA and the Magnuson-
Stevens Act. NMFS does not have discretion to delay implementation of
management measures adopted at ICCAT simply because we anticipate there
may be additional or different ICCAT recommendations in the future.
This action does not implement a unilateral rebuilding plan in U.S.
waters for shortfin mako sharks. This action establishes the foundation
for an international, ICCAT-recommended rebuilding plan, understanding
that ICCAT intends to adopt such a plan in the future and that the
United States will advocate for its development at that forum.
Regarding the comment on the two-year timeframe to implement
management measures being a reason to delay implementation, we note
that we have an obligation to implement the measures under ATCA and the
ICCAT treaty, and that the Magnuson-Stevens Act requires NMFS to take
measures to end overfishing and to rebuild the stocks. The regulatory
process to amend the 2006 Consolidated HMS FMP is a lengthy process
involving significant public input and review; the two-year reference
in the Magnuson-Stevens Act is not to be read as a delay in starting
that process, which could prevent measures from being timely
implemented. Section 304(e)(6) allows for interim measures to reduce
overfishing to be put in place until a FMP amendment can be finalized;
this section of the Magnuson-Stevens Act only allows for these interim
measures to be put in place pursuant to section 305(c), which limits
the amount of time emergency measures can be effective to 366 days.
Based on these regulations, NMFS published the emergency interim final
rule per the authority in sections 305(c) and 304(e)(6) of the
Magnuson-Stevens Act, and is implementing long-term management measures
to address overfishing and establish a foundation for rebuilding
shortfin mako sharks with Amendment 11, consistent with the Magnuson-
Stevens Act.
Comment 4: NMFS received comments in support of adding a sunset
clause to this rulemaking, which would remove regulations implemented
by Amendment 11 if ICCAT makes changes to Recommendation 17-08.
Response: A ``sunset clause'' on regulations to address overfishing
of shortfin mako sharks would not be consistent with the ICCAT
recommendation, or the need to rebuild the stock, which could take
decades based on the 2017 stock assessment. If ICCAT recommends changes
to management measures in the future, NMFS would implement necessary
and appropriate responsive regulatory changes at that time, consistent
with applicable laws.
Comment 5: NMFS received comments regarding the implementation of
the ICCAT regulations and fishing operations by other countries. The
commenters had concerns that other countries are not implementing the
Recommendation and about the pace of the U.S. implementation when
compared to other countries. Commenters also wondered if other ICCAT
countries have electronic monitoring systems or observers for their
fleets. In addition, the commenters believe that U.S. fishermen will be
held accountable for an excessive share of the conservation burden in
future ICCAT management measures.
Response: NMFS acknowledges that countries other than the United
States are responsible for the majority of North Atlantic shortfin mako
shark fishing mortality, hence the need for international coordination
through ICCAT on measures to end overfishing and rebuild the stock.
Regardless of other countries' capability to adequately implement and
enforce ICCAT recommendations, the United States remains obligated
under ATCA to implement ICCAT recommendations. As a responsible party
to ICCAT, NMFS will continue to work collaboratively within the ICCAT
process and advocate for an effective international rebuilding plan,
emphasizing the need for all parties to address their relative share of
contributions to fishing mortality and for equitable management
measures.
Comment 6: NMFS should implement an EFH designation for shortfin
mako sharks.
Response: NMFS has recently updated EFH designations for shortfin
mako sharks under Amendment 10 to the 2006 Consolidated HMS FMP. This
process was initiated with the publication of the draft Atlantic HMS 5
Year Review on March 5, 2015 (80 FR 11981). In this review, NMFS
identified new literature and data that should be considered in EFH
delineation exercises, and recommended updating boundaries for shortfin
mako sharks. There was insufficient information available per the
guidelines listed at Sec. 600.815(a)(8)) to warrant a Habitat Area of
Particular Concern for shortfin mako sharks. NMFS published a draft
Environmental Assessment, which included proposed updates for shortfin
mako shark EFH, on September 8, 2016 (81 FR 62100). NMFS received a
number of written comments and comments at public meetings. Many
comments included suggestions for EFH boundaries based on academic
research. NMFS completed a review of EFH-related literature in
developing the FEIS (see Chapter 3 and Chapter 4 of Amendment 10 for a
review of shortfin mako habitat and biology, and EFH impacts,
respectively), and did not identify sufficient literature warranting
changes to the recently updated EFH boundaries for shortfin mako
sharks. However new data from ongoing surveys, research, and tagging
programs was used to update EFH boundaries. EFH updates for shortfin
mako sharks were finalized September 6, 2017 (82 FR 42329). Maps of
final EFH boundaries for shortfin mako are available in Appendix G of
the Final Environmental Assessment. EFH boundaries may also be viewed
in the EFH Mapper, an online dynamic mapping tool maintained by the
NMFS Office of Habitat Conservation (https://www.habitat.noaa.gov/protection/efh/efhmapper/). This office also maintains an EFH Data
Inventory, which includes shapefiles of EFH boundaries that may be
downloaded by the public (https://www.habitat.noaa.gov/protection/efh/newInv/). The next 5-year review process for HMS EFH will be
initiated in 2022.
Comment 7: NMFS received several comments suggesting that
management measures for shortfin mako sharks should be more restrictive
than those implemented in this rulemaking, including prohibiting all
retention of shortfin mako sharks, or other more restrictive measures,
as the science recommends.
Response: NMFS disagrees that more restrictive measures are
required or necessary at this time. The management measures in
Amendment 11 are consistent with those recommended in ICCAT
Recommendation 17-08 and with NMFS' obligations to address overfishing
and rebuilding, understanding that the stock is fished internationally
and requires international measures to effectively address these
issues. The selected measures are expected to reduce U.S. shortfin mako
shark catch consistent with the SCRS recommendation (72-79 percent),
while still permitting fishermen to retain shortfin mako sharks under
limited circumstances. Given the species' North Atlantic-wide range and
that United States catches constitute only approximately nine percent
of total North Atlantic shortfin mako shark catch, the United States
cannot unilaterally end overfishing and rebuild the stock through
domestic regulations alone, even if there were to be a total
prohibition on possession (which has not been recommended by ICCAT).
[[Page 5362]]
Ending overfishing and rebuilding the stock can only be accomplished
through international coordination with nations that harvest the
majority of shortfin mako sharks. NMFS will work with ICCAT members to
evaluate the effectiveness of these measures, update stock assessment
projections, establish a rebuilding plan, and develop additional
measures if necessary.
Comment 8: NMFS received comments in support of the proposed
preferred commercial alternative (A2), as well as other comments that
suggested modifications to Alternative A2. Several commenters along
with the State of Georgia and the South Atlantic and New England
Fishery Management Councils supported Alternative A2 (the preferred
Alternative at the proposed rule stage) since this Alternative is
consistent with ICCAT Recommendation 17-08, utilized electronic
monitoring, and allowed NMFS to collect real time landings and
additional data. NMFS also received comments including from the State
of North Carolina, Commonwealth of Massachusetts, and HMS Advisory
Panel members supporting Alternative A2 with modifications.
Specifically, the State of North Carolina along with other individuals
suggested a modification that would allow the retention of dead
shortfin mako sharks caught as bycatch in gillnet and bottom longline
fisheries. The Commonwealth of Massachusetts and some HMS Advisory
Panel members suggested a modification that would allow the retention
of dead shortfin mako sharks by any vessel as long as there is an
electronic monitoring system or an observer on board the vessel,
similar to Alternative A5. These commenters also supported Alternative
A3, which would allow vessels the option to opt out of the electronic
monitoring system review.
Response: ICCAT Recommendation 17-08 included a variety of measures
to reduce shortfin mako shark fishing mortality and to increase live
releases in response to the 2017 ICCAT North Atlantic shortfin mako
shark stock assessment. Among these measures was the option to require
the release of shortfin mako sharks brought to the vessel alive in
ICCAT fisheries. This option also allows for the retention of shortfin
mako sharks in ICCAT fisheries that are dead at haulback, provided an
electronic monitoring system is installed, or an observer is on board
to verify the disposition of the shark. In Draft Amendment 11, NMFS
preferred to implement Alternative A2, which limited the retention of
dead shortfin mako sharks to those caught on vessels with an electronic
monitoring system. While the draft amendment preferred alternative did
not limit the gear types that could be used to catch and retain dead
shortfin mako sharks, the requirement to have an electronic monitoring
system installed largely limited the measure to pelagic longline
vessels since these vessels are already required to have electronic
monitoring systems. Alternative A2 would satisfy the requirements of
Recommendation 17-08 and also decrease fishing mortality of shortfin
mako sharks. A large number of commenters expressed support for this
measure. A full analysis of the ecological and socioeconomic impacts
for Alternative A2 is provided in Chapter 4 of the FEIS.
However, during the public comment period, commenters that
expressed support for the preferred Alternative A2 in Draft Amendment
11 also voiced support for allowing retention of dead shortfin mako
sharks in other, non-ICCAT fishery gear types. Although Alternative A2
did not limit the ability to retain dead shortfin mako sharks to
pelagic longline vessels, the requirement to install a costly
electronic monitoring system to do so may have effectively limited the
allowance for retention to the pelagic longline fishery. HMS-permitted
pelagic longline vessels are already required to have electronic
monitoring systems on board, but vessels using other gear types are
unlikely to install the costly system in order to retain shortfin mako
sharks, especially considering the relatively low ex-vessel value.
Thus, the practical effect of Alternative A2 could be to limit the
measure to pelagic longline vessels. To address the public comments on
the Proposed Rule for Amendment 11, NMFS is implementing Alternative
A7, an alternative added and analyzed in the FEIS and adopted in this
final rule. Alternative A7 is a slight modification and outgrowth of
Alternative A2. Under preferred Alternative A7, shortfin mako sharks
caught using gillnet, bottom longline, or pelagic longline gear on
properly-permitted vessels could be retained, provided they are dead at
haulback. In the case of pelagic longline vessels, an electronic
monitoring system would still be required, as proposed, but an
electronic monitoring system would not be required on vessels that use
bottom longline or gillnet gear. To be responsive to public comments,
NMFS reviewed the available data for shortfin mako shark interactions
by vessels that use bottom longline and gillnet gear. After reviewing
the information and considering past actions, NMFS decided to add
Alternative A7 as the preferred alternative. One of the alternatives in
the proposed rule analyzed and considered retention within the bottom
longline and gillnet fisheries, and public comment on the alternatives
resulted in the development of Alternative A7. Commenters thus could
reasonably have anticipated this alternative, which is a logical
outgrowth of the alternatives considered, and is consistent with the
ICCAT measure's application to sharks ``caught in association with
ICCAT fisheries.'' This alternative is largely the same as Alternative
A2 except that it allows retention of dead shortfin mako sharks in the
bottom longline and the gillnet fisheries without requiring an observer
or electronic monitoring system on board. Shortfin mako sharks are
rarely caught with bottom longline and gillnet gear. Based on observer
data, only 40 shortfin mako sharks were caught with bottom longline and
gillnet gear from 2012 to 2017. Due to the low number of observed
interactions, it is doubtful any of these landings were the result of
targeted fishing so it is unlikely more could be done to avoid them.
NMFS will also continue to track landings and consider additional
measures if it appeared that an increase in retention results from this
action, which is extremely unlikely. Retaining an additional six to
seven dead sharks per year will have no additional negative effects on
the stock than considered in the proposed rule, and the United States
will still achieve the needed reductions in mortality with this
alternative. In addition, allowing retention by these gear types will
reduce regulatory dead discards in the non-ICCAT fisheries.
No other commercial gear types would be able to land shortfin mako
sharks under this alternative. While it is possible for other
commercial gears to catch shortfin mako sharks (e.g., rod and reel and
bandit gear), these gears are primarily recreational and are rarely
used to fish for sharks commercially. Buoy gear in particular can
interact with shortfin mako sharks but is not an authorized gear; this
rule does not change that. Under this alternative, all shortfin mako
sharks would need to be released if caught commercially on these other
commercial gears, with the exception described below for those vessels
that hold both a commercial shark permit and a permit with a shark
endorsement that allows for recreational shark landings. This approach
is consistent with previous rulemakings that implemented ICCAT
recommendations for sharks (e.g., prohibiting retention of silky,
hammerhead, oceanic whitetip, or porbeagle sharks in ICCAT fisheries:
76
[[Page 5363]]
FR 53652, August 29, 2011; 77 FR 60632, October 4, 2012; 81 FR 57803,
August 24, 2016). In those cases, NMFS applied ICCAT measures for
sharks only to the pelagic longline fishery and the handgear fisheries
when swordfish or tunas are retained because they are considered ICCAT
fisheries for tunas and tuna-like species. NMFS consistently determined
that U.S. bottom longline and gillnet vessels are not part of an ICCAT
fishery because these gears do not regularly catch or land ICCAT
managed species such as swordfish or tunas. In other words, Alternative
A7, which would allow landings of dead shortfin mako sharks caught by
these non-ICCAT fishery gear types, is consistent with past U.S.
actions.
Additionally, ICCAT Recommendation 17-08 allows retention of
shortfin mako sharks that are dead at haulback without the verification
of electronic monitoring or observers in certain limited circumstances,
including for vessels under 12 meters. Most vessels that have a
Directed shark LAP and use bottom longline or gillnet gear have vessel
lengths that are below 12 meters. In 2017, bottom longline vessels that
interacted with sharks (based on coastal fisheries and HMS logbook
reports) averaged 11.4 meters in length. In 2017, gillnet vessels that
interacted with sharks (based on coastal fisheries and HMS logbook
reports) averaged 9.6 meters in length. Thus, given past rulemakings
and given the length of most vessels that target sharks, allowing
landings of dead shortfin mako sharks by these other gear types is
appropriate and consistent with ICCAT Recommendation 17-08.
Comment 9: NMFS received a suggestion for potential management
measures if more commercial regulations are needed to protect the
shortfin mako stock. The commenter suggested that NMFS implement a
seasonal incidental limit of 18 shortfin mako sharks per trip during
the summer months.
Response: The preferred alternatives in Final Amendment 11 are
consistent with ICCAT Recommendation 17-08 and are designed to address
the United States' contribution to the overfishing of shortfin mako
sharks. If future ICCAT SCRS analyses determine that additional
shortfin mako shark mortality reductions are needed, NMFS would
consider other options, consistent with any ICCAT recommendations. At
this time, a seasonal commercial limit of shortfin mako sharks is not
consistent with ICCAT Recommendation 17-08 and it is unclear if it
would achieve mortality reduction targets.
Comment 10: NMFS received a comment that the combination of
preferred alternatives at the proposed rule stage, specifically
Alternatives A2 and B3, would cause commercial shark permits that are
held with HMS Charter/Headboat permits to be ``worthless.'' Such
fishermen hold both permits to allow them to sell sharks caught as
bycatch when fishing for tuna with handline gear. The proposed
combination of alternatives would require such a dual-permitted vessel
to use only pelagic longline gear, to have an electronic monitoring
system, and to only land shortfin mako sharks that were greater than 83
inches fork length that were dead at haulback. These requirements would
apply even when fishing on a for-hire trip.
Response: The commenter was correct that under the proposed
alternatives it was unlikely that a dual-permitted vessel (which could
include a variety of permits including, for example, those vessels that
hold a commercial shark permit and an Atlantic Tunas General category
permit that allows for retention of sharks when participating in a
registered tournament) could land shortfin mako sharks. Additionally,
NMFS realized this concern about permit combinations could apply to
many combinations of the commercial and recreational alternatives
considered. NMFS did not intend for this effect as a result of the
proposed rule. As such, in the FEIS, NMFS is clarifying how the
recreational limits would apply to the few individuals who hold a
commercial shark vessel permit in addition to one of a variety of other
vessel permits, such as HMS Charter/Headboat, that allow for
recreational landings of sharks. These vessels generally fish with rod
and reel or other handgear as opposed to pelagic longline, bottom
longline, or gillnet gear. However, these vessels are part of the ICCAT
fishery as they regularly target tunas, billfish, and swordfish. For
the sake of clarity, NMFS would restrict these permit holders to the
recreational shark requirements when shortfin mako sharks are onboard
and prohibit them from selling any sharks when recreationally retaining
shortfin mako sharks.
Comment 11: NMFS received comments both in support of and opposed
to Alternative B3, which was the preferred alternative at the proposed
rule stage. Some commenters, along with the Commonwealth of
Massachusetts and the New England Fishery Management Council, supported
Alternative B2 and management measures to protect shortfin mako sharks
until they reach maturity. These commenters generally felt that the
United States strongly supported the adopted size restrictions at
ICCAT, and that NMFS should not now go beyond the recommendations.
These commenters noted that the same minimum size under the emergency
rule reduced U.S. landings beyond the suggested reduction of 72 to 79
percent. Other commenters noted that NMFS underestimated potential
reductions in landings in their analysis of the recreational
alternatives because they did not account for reductions in the number
of trips that would target shortfin mako sharks. The State of North
Carolina supported Alternative B3 and specifically noted that if NMFS
chooses Alternative B2 instead, NMFS should include shark sex
identification facts on the HMS shark endorsement quiz and other
outreach material. Commenters from the Gulf of Mexico supported
Alternative B3 because they commonly interact with shortfin mako sharks
larger than 83 inches fork length (FL). NMFS also received comments
from individuals as well as the State of Georgia and the South Atlantic
Fishery Management Council in support of the Alternative B3, which
would establish a single recreational size limit of 83 inches FL, and
is consistent with the measure established in the emergency rule. In
general, these commenters felt the one size limit in Alternative B3
would remove any confusion recreational fishermen may have in
identifying shortfin mako sharks by sex. Additionally, NMFS received
requests for NMFS to consider other minimum sizes that are smaller than
the preferred alternative of 83 inches FL. These commenters felt that
NMFS should protect the larger, breeding female sharks over 83 inches
FL and implement a smaller minimum size, such as 72 or 75 inches FL,
for male sharks since those sharks still provide a decent amount of
meat.
Response: Based on the public comment and current recreational
estimated harvest under the emergency regulations (83 inches FL for all
shortfin mako sharks), NMFS has decided to change the preferred
alternative in the Final Amendment 11 to Alternative B2, which
establishes different minimum sizes for male and female shortfin mako
shark retention (71 inches FL size limit for male and 83 inches FL size
limit for female shortfin mako sharks). In Draft Amendment 11 and the
emergency interim final rule, the minimum size limit was increased to
83 inches FL for both males and females (Alternative B3) to
significantly reduce shortfin mako
[[Page 5364]]
shark recreational mortality and address overfishing. One size was used
for both sexes for reasons discussed in the emergency interim final
rule and proposed rule. Updated data gathered from operations occurring
under the emergency interim rule provisions indicate, however, that
this approach would be unnecessarily restrictive for the longer term.
While the shortfin mako shark landings under the 83-inch FL size limit
met the suggested reduction target by weight, the size limit exceeded
the target reduction in numbers of sharks harvested. As described in
Chapter 4 of the FEIS, Large Pelagics Survey (LPS) data indicated there
was a substantial reduction in recreational trips targeting shortfin
mako sharks as a result of implementation of the emergency interim
rule. The recreational landings data observed in the LPS suggest that
the separate size limits for male and female sharks now preferred under
Alternative B2 should still accomplish the suggested mortality
reduction targets while having less detrimental economic impacts on the
recreational shark fishery.
Furthermore, studies have indicated that protecting sub-adult
sharks is key to conserving and rebuilding shark populations (see
Chapter 4 of the FEIS). Sub-adults are generally those juvenile sharks
that are a year or two away from becoming mature adults. While the now-
preferred Alternative B2 will allow greater harvest of male shortfin
mako sharks, those sharks will still be mature individuals as 71 inches
FL is the size of maturity for male shortfin mako sharks. Given that
studies have indicated that protecting sub-adult sharks is key to
conserving and rebuilding shark populations, Alternative B2 ensures
that sub-adults would still be adequately protected by establishing
minimum size limits for male and female sharks based on their size at
maturity. NMFS also anticipates that the now-preferred Alternative B2,
which allows recreational fishermen the opportunity to harvest smaller
male sharks, will help relieve fishing pressure on the larger female
sharks, which were estimated to comprise approximately 75 percent of
the harvest under the preferred alternative from the emergency interim
final rule (Alternative B3), which established only one size for both
males and females. Landings data from the LPS shows that female
shortfin mako sharks over 83 inches FL historically made up only about
12 percent of the overall harvest. Under a single 83 inches FL size
limit it is highly likely most vessels that successfully harvest a
shark over 83 inches FL will have already caught and released several
smaller male sharks first. Since recreational fishermen are only
allowed to harvest one shortfin mako shark per vessel per day,
establishing a separate and significantly smaller size limit for male
sharks will greatly increase the probability that the first legal sized
shark a vessel interacts with will thus be a male shark which should
lead to fewer female sharks ultimately being harvested.
Since the final preferred alternative (Alternative B2) establishes
a different minimum size limit for each sex of shortfin mako shark
species, NMFS intends to include information on properly distinguishing
between male and female sharks on all related outreach materials, web
page, and the shark endorsement video (which is mandatory for all HMS
permit holders that wish to retain sharks recreationally). NMFS also
expects to provide such information to registered HMS shark tournaments
to make sure participants are aware of the separate size limits and how
to distinguish between male and female sharks. NMFS will continue to
monitor recreational landings of shortfin mako sharks, and would take
action to increase the minimum size limit if recreational landings
targets are not meet or if enforcing separate size limits by sex proves
to be impractical.
Comment 12: NMFS received a comment stating that the seasonal
recreational alternatives would not allow Gulf of Mexico fishermen
ample opportunity to land shortfin mako sharks since they primarily
target the species outside of the months considered in the alternative.
Response: NMFS did not prefer Alternative B6, or any of its sub-
alternatives, in the proposed rule due to the potential for inequitable
fishing opportunities this alternative could create in terms of
regional access to the shortfin mako shark recreational fishery. NMFS
now prefers Alternative B2, which establishes a minimum size limit of
71 inches FL for male and 83 inches FL for female shortfin mako sharks,
which would mean all recreational fishermen would have the same
regulations regardless of where and when they decide to fish.
Comment 13: NMFS received comments in support of the no action
recreational alternative (Alternative B1). Specifically, commenters
supported keeping the shortfin mako shark recreational minimum size at
status quo (54 inches FL) since they feel the population decline is not
due to the recreational fishery and the recreational fishery should not
be impacted by other fisheries.
Response: While NMFS recognizes that the U.S. recreational fishery
for shortfin mako sharks only makes up a small portion of the overall
international harvest, its contribution to the total U.S. catch is
larger than the commercial fishery landings. According to data
presented in the Final Amendment 11, the U.S. recreational fishery
accounts on average for 58 percent of the total U.S. catch, while the
commercial fishery accounts on average for 42 percent. Therefore, U.S.
recreational fisheries have a significant role to play in reducing
fishing mortality on shortfin mako sharks, and must be included in
management of this overfished stock. Furthermore, the no action
alternative would fail to meet the minimum requirements set forth in
ICCAT Recommendation 17-08 and would be inconsistent with U.S.
obligations under the ICCAT treaty, ATCA, and other legal requirements.
Comment 14: NMFS received comments in support of Alternative B8,
which would establish a tagging program to implement a per season limit
for recreational fishermen.
Response: At this time, NMFS does not intend to implement a tagging
program for recreationally harvested shortfin mako sharks since the
final preferred alternative (Alternative B2) to establish minimum sizes
would sufficiently reduce the recreational harvest levels. In addition,
tagging programs are complicated to implement for a variety of reasons
including the need to assign a limited number of tags via raffle, and
the extra time and resources required to track them when reported. As
discussed in the FEIS, NMFS would need to assign tags via raffle as the
number of HMS permit holders with shark endorsements far exceeds the
number of shortfin mako sharks that could be harvested and still meet
the recommended reduction target of 72 to 79 percent. For these
reasons, NMFS does not prefer a tagging program at this time.
Comment 15: NMFS received a comment suggesting that we change the
shortfin mako shark recreational fishery to be similar to the bluefin
tuna recreational fishery regulations. The commenter suggested a
shortfin mako shark recreational fishery where permit holders would be
restricted to one trophy shark over 83 inches FL, one smaller shark
between 65 to 83 inches FL, and a 2 shark per season limit per
recreational shark permit.
Response: The management regime suggested in this comment would be
similar to the implementation of a
[[Page 5365]]
tagging program in that such a program would require NMFS to monitor a
seasonal bag limit. Similar to the tagging program, NMFS has determined
that such a management program is unnecessary to accomplish the
recommended reduction in landings as the minimum size limits currently
under consideration would reduce overall harvest to far fewer than two
sharks per permitted vessel per season. Furthermore, a 65 inch FL size
limit for shortfin mako sharks would be below the size limits
stipulated in ICCAT Recommendation 17-08, and would fail to meet U.S.
obligations to implement binding ICCAT recommendations under ATCA.
Comment 16: NMFS received support and opposition for the preferred
alternative (Alternative B9) to implement circle hooks in the
recreational fishery. Some commenters along with the Commonwealth of
Massachusetts and the South Atlantic and New England Fishery Management
Councils supported the preferred alternative due to the benefits of
live release of sharks that may provide enhanced survivorship in some
species. The State of Georgia opposed the implementation of circle
hooks in the recreational fishery for sharks in federal waters due to
its ``questionable administration by law enforcement officers'' and the
unnecessary burden it will place on recreational anglers. In addition,
the State of Georgia noted that it does not intend to adopt circle
hooks in state waters.
Response: Research shows that the use of circle hooks reduces gut-
hooking and increases post-release survival in shortfin mako sharks.
French et al. (2015) examined the effects of recreational fishing
techniques, including hook type, on shortfin mako sharks and found that
circle hooks were more likely to hook shortfin mako sharks in the jaw
compared to J-hooks. In the study, circle hooks were most likely to
hook in the jaw (83 percent of the time) while J-hooks most commonly
hooked in the throat (33 percent of the time) or gut (27 percent of the
time). J-hooks only hooked in the jaw of shortfin mako sharks 20
percent of the time. Jaw-hooking is correlated with increased odds of
post release survival. For these and other reasons (e.g., endangered
species interactions), NMFS prefers this alternative. In addition,
circle hooks are already required by HMS permitted commercial and
recreational, except for north of 41[deg]43' N latitude (near Chatham,
Massachusetts), fishermen.
While NMFS recognizes the State of Georgia's concern regarding
enforceability, circle hooks have been required by HMS recreational
permit holders since January 1, 2018, and other states, such as the
State of New York, also requires the use of circle hooks when fishing
for sharks. In Amendment 5b to the 2006 Consolidated HMS FMP, NMFS
required the use of non-offset, non-stainless steel circle hooks by HMS
recreational permit holders with a shark endorsement when fishing for
sharks recreationally, except when fishing with flies or artificial
lures, in federal waters south of 41[deg]43' N latitude (near Chatham,
Massachusetts). The final preferred Alternative (Alternative B9) would
remove this line and require circle hooks when fishing recreationally
for sharks in all areas, except when fishing with flies or artificial
lures.
Comment 17: NMFS received a comment inquiring whether the new MRIP
estimates would impact this rulemaking or future stock assessment.
Response: Recently, NMFS released new MRIP effort and catch
estimate time series following the implementation of the new Fishing
Effort Survey (FES) designed for the collection of private boat and
shore-based fishing effort data, and its calibration with the data
collected by the historic Coastal Household Telephone Survey (CHTS).
The implications of the revised estimates on all managed species will
not be fully understood for several years until they make their way
through the rigorous scientific stock assessment process. In the coming
years, the new and revised data will be incorporated into stock
assessments at the domestic and international level as appropriate.
However, NOAA Fisheries' primary source of recreational catch data for
shortfin mako sharks is the Large Pelagic Survey (LPS) which does not
rely on the FES, and as a result the estimates generated by the LPS
used in this rulemaking have not changed.
Comment 18: NMFS received a comment stating that banning tournament
fishing for sharks would help to end overfishing, and that NMFS would
be justified in doing so on the grounds that tournament awards add a
commercial component to what is supposed to be a recreational fishery.
The commenter also stated that recreationally harvested fish should
only be used for personal consumption, and not monetized.
Response: While tournaments do make up a significant portion of the
recreational shark fishery, NMFS is not in favor of prohibiting shark
tournaments as a means to address overfishing of shortfin mako sharks
for a number of reasons. First, tournaments can provide significant
economic benefits to the coastal communities in which they are held.
Second, banning tournament or sport fishing while still allowing
recreational harvest would constitute an inequitable access of the
resource to the problem of overfishing between tournament and non-
tournament recreational fishermen, and would set a precedent that would
conflict with the management of other U.S. fisheries. Retention of HMS,
including shortfin mako sharks submitted for weigh-in to tournaments,
is authorized under the regulations by the permitted vessel that caught
the fish. Even in cases where anglers donate their fish to the
tournament, the tournament is not allowed to sell the fish, but may
only donate the fish for human consumption to food banks or other
charities.
For HMS fisheries, most tournament participants hold recreational
permits or commercial permits that only allow for recreational landings
of sharks when used during a registered HMS tournament. None of these
participants are allowed to sell their catch. Many commercial
businesses are associated with recreational fisheries including for-
hire vessels, bait and tackle shops, and fishing guides. Like
tournaments, all of these operations service recreational anglers. The
distinction between recreational and commercial fishing lies solely in
whether the fish themselves are sold commercially, not in whether a
business associated with an activity is providing a commercial service.
Many shark tournaments are already moving to catch-and-release formats,
or are shying away from targeting shark species that are not widely
considered to be edible.
Comment 19: NMFS received support and opposition for the preferred
alternative of no action Alternative C1. Some commenters along with the
Commonwealth of Massachusetts, State of Georgia, and South Atlantic
Fishery Management Council supported the preferred alternative since it
would not add any additional reporting requirements for fishermen.
However, commenters also were concerned that some registered HMS
tournaments are currently not required to report their catches of all
HMS. Some commenters opposed the preferred alternative since it would
create inconsistency with the SCRS advice to gather more data and
information on shortfin mako sharks and therefore would negatively
impact science and stock assessments. Some individuals along with the
Mid-Atlantic Fishery Management Council suggested that NMFS should
implement mandatory reporting for all recreationally landed and
discarded shortfin mako sharks. The Mid-Atlantic
[[Page 5366]]
Fishery Management Council stated that it is imperative to collect data
from commercial and recreational fishermen on landings and discards.
Other commenters would like equivalent monitoring and accountability
requirements for all U.S. HMS fisheries, and to fully and accurately
account for all sources of fishing mortality.
Response: There are already a number of reporting requirements
under current HMS regulations for commercial and recreational fishermen
fishing for shortfin mako sharks. HMS commercial fishermen report
shortfin mako shark catches through vessel logbooks along with dealer
reporting of landings. Under Alternative C1, HMS recreational anglers
fishing from Maine to Virginia would continue to be required to report
shortfin mako shark landings and releases if intercepted by the LPS,
and data would continue to be collected on shortfin mako shark catches
by the APIS, which is part of MRIP. As of January 1, 2019, all
registered HMS tournaments will be selected for tournament reporting,
which should account for a significant component of recreational
shortfin mako shark landings (83 FR 63831; December 12, 2018). In
addition, most for-hire vessels fishing in the federal waters in the
Mid-Atlantic area (New York to New Carolina) are currently required by
the Mid-Atlantic Fishery Management Council to submit electronic vessel
trip reports for all their trips within 24 hours, thus providing
another major data stream for shortfin mako shark landings. These
current reporting systems will allow NMFS to effectively monitor the
recreational harvest of the stock using a combination of traditional
intercept surveys, tournament reporting, and electronic reporting
making the implementation of mandatory 24-hour reporting unnecessary at
this time.
NMFS understands that some constituents do not think there is
equitable reporting across HMS fisheries; however, the current
reporting systems mentioned above should account for all sources of
fishing mortality for shortfin mako sharks. NMFS will continue to
monitor the landings by commercial and recreational fishermen to
determine if the current reporting systems are sufficiently accounting
for shortfin mako shark mortality.
Comment 20: NMFS received a comment in support of requiring
mandatory reporting with vessel monitoring systems (VMS) if it would
simplify commercial fishermen's reporting burden, improve the reporting
of HMS catches across all gears, and improve scientific data. The
commenters were not supportive of the alternative that would create
another unnecessary burden on commercial fishermen.
Response: NMFS agrees that requiring mandatory reporting of
shortfin mako sharks via VMS could potentially, and unnecessarily,
increase burden to HMS commercial vessels that already report in other
ways (vessel logbooks, dealer reports of landings, and electronic
monitoring system) that are sufficient reporting systems for improving
data collection for shortfin mako sharks. In addition, given the
current reporting requirements for all HMS commercial vessels that
already enable inseason monitoring and management of shortfin mako
sharks, NMFS did not prefer this alternative at this time. Furthermore,
NMFS is already implementing electronic HMS logbooks on a voluntary
basis to improve the timeliness of reporting, and provide data for
management.
Comment 21: NMFS received support and opposition for the preferred
alternative. Some commenters along with the Commonwealth of
Massachusetts, the State of Georgia, and the South Atlantic and Mid-
Atlantic Fishery Management Councils supported the preferred
alternative to develop an international rebuilding plan with ICCAT to
assist with rebuilding the stock and work with other countries to
implement international management measures. A commenter who opposed
the preferred alternative wants NMFS to implement a domestic rebuilding
plan along with the international plan, while other commenters prefer
that NMFS wait until ICCAT takes further action before finalizing the
rebuilding plan.
Response: North Atlantic shortfin mako shark distribution spans a
large portion of the North Atlantic Ocean basin and many countries
besides the United States interact with the species. Therefore, NMFS
believes that addressing overfishing and preventing an overfished
status can only effectively be accomplished through international
efforts where other countries that have large landings of shortfin mako
sharks actively and equitably participate in mortality reduction and
rebuilding plan discussions. Because of the small U.S. contribution to
North Atlantic shortfin mako shark mortality, domestic reductions of
shortfin mako shark mortality alone would not end overfishing of the
entire North Atlantic stock. For these reasons and for the reasons
described in response to comment 3 above, NMFS prefers Alternative D3,
which would establish the foundation for developing an international
rebuilding plan for shortfin mako sharks.
Comment 22: NMFS received a comment in support of the alternative
to remove shortfin mako sharks from the pelagic shark management group
and establish a separate management group with quota for the species.
Response: At this time, NMFS does not prefer a shortfin mako shark-
specific quota. ICCAT Recommendation 17-08 did not include individual
country allocations for shortfin mako sharks upon which to base a
domestic quota. It is also not clear that a quota would adequately
protect the stock by reducing mortality because quotas allow for sharks
that are live at haulback to be landed. Also, it is difficult at this
time to determine if setting a species-specific quota for shortfin mako
sharks would have positive ecological benefits for the stock, as this
scenario was not explored in the stock assessment. A species-specific
quota for shortfin mako sharks would require authorized fishermen to
discard all shortfin mako sharks once the quota is reached, potentially
leading to an increase in regulatory discards, which would not result
in decreased mortality of shortfin mako sharks and thus, contribute to
the health of the stock. Additionally, commercially, shortfin mako
sharks are most often caught with pelagic longline gear incidental to
other target catch. Since shortfin mako sharks are rarely targeted,
establishing a shortfin mako shark quota is unlikely to stop incidental
fishing mortality.
NMFS believes that ending overfishing and preventing an overfished
status would be better accomplished through the measures preferred in
final Amendment 11 and through further critical international efforts
where other countries that have large landings of shortfin mako sharks
could participate in mortality reduction discussions instead of a
species-specific quota within the U.S. fisheries. NMFS will continue to
monitor progress in the international forum and the needs of the stock,
as well as whether this action has its intended effect, and will
consider whether additional measures are appropriate in the future.
Comment 23: NMFS received a comment in support of the alternative
to establish bycatch caps for all fisheries that interact with shortfin
mako sharks. Specifically, the commenter noted that NMFS should count
the number of shortfin mako sharks caught in all fisheries, cap the
number of shortfin mako sharks that can be caught, and implement
accountability measures to control, track, and limit the number of
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sh