International Fisheries; Western and Central Pacific Fisheries for Highly Migratory Species; Fishing Limits in Purse Seine and Longline Fisheries, Restrictions on the Use of Fish Aggregating Devices in Purse Seine Fisheries, and Transshipment Prohibitions, 21748-21761 [2018-09896]
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21748
Federal Register / Vol. 83, No. 91 / Thursday, May 10, 2018 / Proposed Rules
National Oceanic and Atmospheric
Administration
50 CFR Part 300
[Docket No. 180209155–8399–01]
RIN 0648–BH77
International Fisheries; Western and
Central Pacific Fisheries for Highly
Migratory Species; Fishing Limits in
Purse Seine and Longline Fisheries,
Restrictions on the Use of Fish
Aggregating Devices in Purse Seine
Fisheries, and Transshipment
Prohibitions
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule; request for
comments.
AGENCY:
NMFS seeks comments on
this proposed rule issued under
authority of the Western and Central
Pacific Fisheries Convention
Implementation Act (WCPFC
Implementation Act). The proposed rule
would implement recent decisions of
the Commission for the Conservation
and Management of Highly Migratory
Fish Stocks in the Western and Central
Pacific Ocean (WCPFC or Commission).
These decisions include the following
management measures: limits on fishing
effort by U.S. purse seine vessels in the
U.S. exclusive economic zone and on
the high seas between the latitudes of
20° N and 20° S in the area of
application of the Convention on the
Conservation and Management of
Highly Migratory Fish Stocks in the
Western and Central Pacific Ocean
(Convention); restrictions regarding the
use of fish aggregating devices (FADs)
for U.S. purse seine fishing vessels;
limits on the catches of bigeye tuna by
U.S. longline vessels in the Convention
area; prohibitions on U.S. vessels used
to fish for highly migratory species from
engaging in transshipment in a
particular area of the high seas (the
Eastern High Seas Special Management
Area or EHSSMA); and removal of
existing reporting requirements for
vessels transiting the EHSSMA. The rule
also would make corrections to outdated
cross references in existing regulatory
text. This action is necessary to satisfy
the obligations of the United States
under the Convention, to which it is a
Contracting Party.
DATES: Comments on the proposed rule
must be submitted in writing by May 25,
2018.
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SUMMARY:
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You may submit comments
on the proposed rule and the regulatory
impact review (RIR) prepared for the
proposed rule, identified by NOAA–
NMFS–2018–0050, by either of the
following methods:
• Electronic submission: Submit all
electronic public comments via the
Federal e-Rulemaking Portal.
1. Go to www.regulations.gov/
#!docketDetail;D=NOAA-NMFS-20180050,
2. Click the ‘‘Comment Now!’’ icon,
complete the required fields, and
3. Enter or attach your comments.
—OR—
• Mail: Submit written comments to
Michael D. Tosatto, Regional
Administrator, NMFS, Pacific Islands
Regional Office (PIRO), 1845 Wasp
Blvd., Building 176, Honolulu, HI
96818.
Instructions: Comments sent by any
other method, to any other address or
individual, or received after the end of
the comment period, might not be
considered by NMFS. All comments
received are a part of the public record
and will generally be posted for public
viewing on www.regulations.gov
without change. All personal identifying
information (e.g., name and address),
confidential business information, or
otherwise sensitive information
submitted voluntarily by the sender will
be publicly accessible. NMFS will
accept anonymous comments (enter ‘‘N/
A’’ in the required fields if you wish to
remain anonymous).
An initial regulatory flexibility
analysis (IRFA) prepared under
authority of the Regulatory Flexibility
Act is included in the Classification
section of the SUPPLEMENTARY
INFORMATION section of this document.
Copies of the RIR, the 2015
programmatic environmental
assessment, and 2012 environmental
assessment prepared for National
Environmental Policy Act (NEPA)
purposes are available at
www.regulations.gov or may be obtained
from Michael D. Tosatto, Regional
Administrator, NMFS PIRO (see address
above).
Written comments regarding the
burden-hour estimates or other aspects
of the collection-of-information
requirements contained in this proposed
rule may be submitted to PIRO at the
address listed above and by email to
OIRA_Submission@omb.eop.gov or fax
to (202) 395–5806.
ADDRESSES:
DEPARTMENT OF COMMERCE
Rini
Ghosh, NMFS PIRO, 808–725–5033.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
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Background on the Convention
The Convention focused on the
conservation and management of
fisheries for highly migratory species
(HMS). The objective of the Convention
is to ensure, through effective
management, the long-term
conservation and sustainable use of
HMS in the Western and Central Pacific
Ocean (WCPO). To accomplish this
objective, the Convention established
the Commission, which includes
Members, Cooperating Non-members,
and Participating Territories
(collectively referred to here as
‘‘members’’). The United States of
America is a Member. American Samoa,
Guam, and the Commonwealth of the
Northern Mariana Islands (CNMI) are
Participating Territories.
As a Contracting Party to the
Convention and a Member of the
Commission, the United States
implements, as appropriate,
conservation and management measures
and other decisions adopted by the
Commission. The WCPFC
Implementation Act (16 U.S.C. 6901 et
seq.), authorizes the Secretary of
Commerce, in consultation with the
Secretary of State and the Secretary of
the Department in which the United
States Coast Guard is operating
(currently the Department of Homeland
Security), to promulgate such
regulations as may be necessary to carry
out the obligations of the United States
under the Convention, including the
decisions of the Commission. The
WCPFC Implementation Act further
provides that the Secretary of Commerce
shall ensure consistency, to the extent
practicable, of fishery management
programs administered under the
WCPFC Implementation Act and the
Magnuson-Stevens Fishery
Conservation and Management Act
(MSA; 16 U.S.C. 1801 et seq.), as well
as other specific laws (see 16 U.S.C.
6905(b)). The Secretary of Commerce
has delegated the authority to
promulgate regulations under the
WCPFC Implementation Act to NMFS.
A map showing the boundaries of the
area of application of the Convention
(Convention Area), which comprises the
majority of the WCPO, can be found on
the WCPFC website at: www.wcpfc.int/
doc/convention-area-map.
Background on the Conservation and
Management Measures
This proposed rule would implement
specific provisions of two recent
WCPFC decisions. The first decision,
Conservation and Management Measure
(CMM) 2017–01, ‘‘Conservation and
Management Measure for Bigeye,
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Yellowfin, and Skipjack Tuna in the
Western and Central Pacific Ocean,’’
was adopted by the Commission at its
fourteenth regular annual session, in
December 2017, and went into effect
February 2018. The provisions of CMM
2017–01 are described in more detail
below. The second decision, CMM
2016–02, ‘‘Conservation and
Management Measures for Eastern High
Seas Pocket Special Management Area,’’
revises a previous measure regarding the
EHSSMA so that vessels are no longer
required to provide reports to the
Commission when entering and exiting
the EHSSMA and also prohibits all
transshipment activities in the area
starting on January 1, 2019.
CMM 2017–01 is the latest in a series
of CMMs devoted to the conservation
and management of tropical tuna stocks,
particularly stocks of bigeye tuna
(Thunnus obesus), yellowfin tuna
(Thunnus albacares), and skipjack tuna
(Katsuwonus pelamis). The stated
purpose of CMM 2017–01 is to provide
for a robust transitional management
regime that ensures the sustainability of
bigeye tuna, yellowfin tuna, and
skipjack tuna in the WCPO pending the
Commission’s establishment of harvest
strategies.
In order to achieve that stated
purpose, CMM 2017–01 includes
provisions for longline and purse seine
vessels that would be implemented in
this proposed rule. For longline vessels,
the CMM includes specific bigeye tuna
catch limits for several WCPFC
members, including the United States.
The CMM provides for a limit of 3,554
metric tons (mt) of bigeye tuna that may
be caught by U.S. longline vessels
fishing in the Convention Area for
calendar year 2018, which is the same
as the U.S. limit in 2016, as specified in
earlier WCPFC decisions. As in previous
WCPFC CMMs on tropical tunas, CMM
2017–01 also requires any overage of the
catch limit to be deducted from the
following year’s limit.
Also as in previous CMMs, no limits
apply to the longline fisheries of the
U.S. Participating Territories of
American Samoa, Guam, and CNMI. In
addition, CMM 2017–01 includes a new
provision for U.S. longline vessels,
stating that catch and effort of U.S.flagged vessels operating under
agreements with the U.S. Participating
Territories shall be attributed to the U.S.
Participating Territories.
For purse seine vessels, CMM 2017–
01 includes several restrictions on the
use of FADs and provides for specific
limits on fishing effort.
The first FAD restriction is similar to
the one included in previous WCPFC
decisions and requires purse seine
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vessels to be prohibited from fishing on
FADs on the high seas and in the
exclusive economic zones (EEZs) in the
Convention Area between the latitudes
of 20° N and 20° S from July 1 through
September 30 of 2018. The second FAD
restriction requires WCPFC members to
establish an additional consecutive twomonth FAD prohibition period on the
high seas in the Convention Area in
2018, in either April and May or
November and December. CMM 2017–
01 also includes provisions encouraging
WCPFC members to use non-entangling
design and materials as well as
biodegradable materials in the
construction of FADs. Finally, CMM
2017–01 includes a provision requiring
that each purse seine vessel have no
more than 350 drifting FADs with
activated instrumented buoys deployed
at sea in the Convention Area at any one
time through February 10, 2021. Under
the CMM, an instrumented buoy is
defined as a buoy with a clearly marked
reference number allowing its
identification and equipped with a
satellite tracking system to monitor its
position. The CMM states that the buoy
shall be activated exclusively on board
the vessel.
Under CMM 2017–01, WCPFC
members must also limit their purse
seine vessels to specific fishing effort
limits. The limits on U.S. purse seine
fishing effort detailed in CMM 2017–01
are similar to limits in previous WCPFC
decisions. The limits are 558 fishing
days in the U.S. EEZ and 1,270 fishing
days on the high seas in the Convention
Area between the latitudes of 20° N and
20° S for each of the calendar years
2018–2020. However, CMM 2017–01
also includes a new provision for 2018
only that allows the United States to
transfer 100 fishing days from its limit
in the U.S. EEZ to its limit on the high
seas, and if the U.S. EEZ limit is reached
by October 1, 2018, the U.S. EEZ limit
will be increased by an additional 100
fishing days, with the expectation that
the catch taken by U.S. flagged vessels
and landed in American Samoa for the
American Samoa canneries is no less
than the volume landed in 2017 plus an
additional 3,500 short tonnes. This new
provision was intended to alleviate the
economic hardship faced by American
Samoa and its canneries when U.S.
purse seine fishing limits are reached,
resulting in fishery closures.
CMM 2017–01 also includes
provisions for purse seine vessels that
were in previous WCPFC decisions and
that have been implemented by NMFS
in regulations that continue in force.
These provisions include requirements
for purse seine vessels to retain all catch
of bigeye tuna, yellowfin tuna, and
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skipjack tuna, for observer coverage on
purse seine vessels, and for vessel
monitoring system requirements for
purse seine vessels during the FAD
closure periods.
Proposed Action
The elements of the proposed rule are
detailed below. The administrative
changes that would be made to correct
outdated references in existing
regulatory text are described at the end.
As described above, some of the
provisions in CMM 2017–01 apply only
to calendar year 2018, while others are
applicable until February 10, 2021.
Because the Commission likely will
continue to implement similar
management measures regarding FADs,
purse seine effort limits, and longline
bigeye tuna catch limits beyond 2018,
and to avoid a lapse in the management
of the fishery, NMFS is proposing to
implement all of the elements of CMM
2017–01 in this proposed rule under the
authority of the WCPFC Implementation
Act, 16 U.S.C. 6904(a), so that they will
remain effective until they are replaced
or amended. Because the Commission
developed CMM 2017–01 as generally a
three-year conservation and
management measure (2018–2020), the
supporting analyses for this rule covers
a three-year time period, understanding
that these analyses would need to be
supplemented should the elements of
the rule remain effective for more than
three years.
Longline Bigeye Tuna Catch Limits
The Commission-adopted longline
bigeye tuna catch limit for the United
States for 2018 is 3,554 mt. As stated
above, CMM 2017–01 reiterates the
provision of earlier CMMs that states
that any catch overage in a given year
shall be deducted from the catch limit
for the following year. The longline
bigeye tuna catch limit for the United
States in 2017 was 3,138 mt (see Interim
Rule; 82 FR 36341, published August 4,
2017). Based on preliminary estimates,
NMFS believes that the 2017 limit might
have been exceeded, but the amount of
the overage, if it occurred, is not yet
known. Thus, NMFS is proposing a
calendar year catch limit of 3,554 mt
that would remain effective until
replaced. However, for 2018, it is
possible that this limit would be
adjusted downward to account for any
overage in 2017; the limit would
similarly be adjusted downward in
future years, should any overages occur.
NMFS will determine the exact amount
of the overage prior to publication of the
final rule and include the exact amount
of the 2018 limit in the final rule.
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The calendar year longline bigeye
tuna catch limit will apply only to U.S.flagged longline vessels operating as
part of the U.S. longline fisheries. The
limit will not apply to U.S. longline
vessels operating as part of the longline
fisheries of American Samoa, CNMI, or
Guam. Existing regulations at 50 CFR
300.224(b), (c), and (d) detail the
manner in which longline-caught bigeye
tuna is attributed among the fisheries of
the United States and the U.S.
Participating Territories.
Consistent with the basis for the
limits prescribed in CMM 2017–01 and
with regulations issued by NMFS to
implement bigeye tuna catch limits in
U.S. longline fisheries as described
below, the catch limit is measured in
terms of retained catches—that is,
bigeye tuna that are caught by longline
gear and retained on board the vessel.
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1. Announcement of the Limit Being
Reached
As set forth under the existing
regulations at 50 CFR 300.224(e), if
NMFS determines that the limit is
expected to be reached in a calendar
year, NMFS will publish a notice in the
Federal Register to announce specific
fishing restrictions that will be effective
from the date the limit is expected to be
reached until the end of the calendar
year. NMFS will publish the notice of
the restrictions at least 7 calendar days
before the effective date to provide
vessel owners and operators with
advance notice. Periodic forecasts of the
date the limit is expected to be reached
will be made available to the public,
such as by posting on a website, to help
vessel owners and operators plan for the
possibility of the limit being reached.
2. Restrictions After the Limit Is
Reached
As set forth under the existing
regulations at 50 CFR 300.224(f), if the
limit is reached, the restrictions that
will be in effect will include the
following:
a. Retain on board, transship, or land
bigeye tuna: Starting on the effective
date of the restrictions and extending
through December 31 of the given
calendar year, it will be prohibited to
use a U.S. fishing vessel to retain on
board, transship, or land bigeye tuna
captured in the Convention Area by
longline gear, except as follows:
First, any bigeye tuna already on
board a fishing vessel upon the effective
date of the restrictions can be retained
on board, transshipped, and/or landed,
provided that they are landed within 14
days after the restrictions become
effective. A vessel that had declared to
NMFS pursuant to 50 CFR 665.803(a)
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that the current trip type is shallowsetting is not subject to this 14-day
landing restriction, so these vessels will
be able to land bigeye tuna more than
14 days after the restrictions become
effective.
Second, bigeye tuna captured by
longline gear can be retained on board,
transshipped, and/or landed if they are
caught by a fishing vessel registered for
use under a valid American Samoa
Longline Limited Access Permit, or if
they are landed in American Samoa,
Guam, or CNMI. However, the bigeye
tuna must not be caught in the portion
of the U.S. EEZ surrounding the
Hawaiian Archipelago, and must be
landed by a U.S. fishing vessel operated
in compliance with a valid permit
issued under 50 CFR 660.707 or
665.801.
Third, bigeye tuna captured by
longline gear can be retained on board,
transshipped, and/or landed if they are
caught by a vessel that is included in a
specified fishing agreement under 50
CFR 665.819(d), in accordance with 50
CFR 300.224(f)(iv).
b. Transshipment of bigeye tuna to
certain vessels: Starting on the effective
date of the restrictions and extending
through December 31 of the calendar
year, it will be prohibited to transship
bigeye tuna caught in the Convention
Area by longline gear to any vessel other
than a U.S. fishing vessel operated in
compliance with a valid permit issued
under 50 CFR 660.707 or 665.801.
c. Fishing inside and outside the
Convention Area: To help ensure
compliance with the restrictions related
to bigeye tuna caught by longline gear
in the Convention Area, two additional,
related prohibitions would be in effect
starting on the effective date of the
restrictions and extending through
December 31 of the calendar year. First,
vessels are prohibited from fishing with
longline gear both inside and outside
the Convention Area during the same
fishing trip, with the exception of a
fishing trip that is in progress at the time
the announced restrictions go into
effect. In that exceptional case, the
vessel still must land any bigeye tuna
taken in the Convention Area within 14
days of the effective date of the
restrictions, as described above. Second,
if a vessel is used to fish using longline
gear outside the Convention Area and
enters the Convention Area at any time
during the same fishing trip, the
longline gear on the fishing vessel must
be stowed in a manner so as not to be
readily available for fishing while the
vessel is in the Convention Area,
specifically, the hooks, branch or
dropper lines, and floats used to buoy
the mainline must be stowed and not
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available for immediate use, and any
power-operated mainline hauler on
deck must be covered in such a manner
that it is not readily available for use.
These two prohibitions do not apply to
the following vessels: (1) Vessels on
declared shallow-setting trips pursuant
to 50 CFR 665.803(a); and (2) vessels
operating for the purposes of this rule as
part of the longline fisheries of
American Samoa, Guam, or the CNMI.
This second group includes vessels
registered for use under valid American
Samoa Longline Limited Access Permits
and vessels landing their bigeye tuna
catch in one of the three U.S.
Participating Territories, so long as
these vessels conduct fishing activities
in accordance with the conditions
described above, and vessels included
in a specified fishing agreement under
50 CFR 665.819(d), in accordance with
50 CFR 300.224(f)(iv).
FAD Restrictions
In accordance with CMM 2017–01,
NMFS proposes to establish a FAD
prohibition period from July through
September in each calendar year in the
Convention Area between the latitudes
of 20° N and 20° S (inclusive of the
EEZs and high seas in the Convention
Area). Regarding the additional
consecutive two-month FAD prohibition
period on the high seas in the
Convention Area, after considering the
objectives of CMM 2017–01, the
expected economic impacts on U.S.
fishing operations and the nation as a
whole, and expected environmental and
other effects, NMFS expects that a high
seas FAD prohibition period in
November and December may be
somewhat more cost-effective than a
FAD prohibition period in April and
May. For this reason, NMFS is
proposing to implement the high seas
FAD prohibition period in November
and December for each calendar year.
We specifically seek public comment on
which option is more appropriate. A
comparison of the two options’ expected
direct economic impacts on affected
fishing businesses is provided in the
RIR.
As currently defined in 50 CFR
300.211, a FAD is ‘‘any artificial or
natural floating object, whether
anchored or not and whether situated at
the water surface or not, that is capable
of aggregating fish, as well as any object
used for that purpose that is situated on
board a vessel or otherwise out of the
water. The definition of FAD does not
include a vessel.’’ Under this proposed
rule, the regulatory definition of a FAD
would not change. Although the
definition of a FAD does not include a
vessel, the restrictions during the FAD
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prohibition periods would include
certain activities related to fish that
have aggregated in association with a
vessel, or drawn by a vessel, as
described below.
The prohibitions applicable to these
proposed FAD-related measures are in
existing regulations at 50 CFR
300.223(b)(1)(i)–(v). Specifically, during
the July-September FAD prohibition
periods in each calendar year, and on
the high seas in November and
December, owners, operators, and crew
of fishing vessels of the United States
equipped with purse seine gear shall not
do any of the following activities in the
Convention Area in the area between
20° N latitude and 20° S latitude:
(1) Set a purse seine around a FAD or
within one nautical mile of a FAD;
(2) Set a purse seine in a manner
intended to capture fish that have
aggregated in association with a FAD or
a vessel, such as by setting the purse
seine in an area from which a FAD or
a vessel has been moved or removed
within the previous eight hours, setting
the purse seine in an area in which a
FAD has been inspected or handled
within the previous eight hours, or
setting the purse seine in an area into
which fish were drawn by a vessel from
the vicinity of a FAD or a vessel;
(3) Deploy a FAD into the water;
(4) Repair, clean, maintain, or
otherwise service a FAD, including any
electronic equipment used in
association with a FAD, in the water or
on a vessel while at sea, except that a
FAD may be inspected and handled as
needed to identify the FAD, identify and
release incidentally captured animals,
un-foul fishing gear, or prevent damage
to property or risk to human safety; and
a FAD may be removed from the water
and if removed may be cleaned,
provided that it is not returned to the
water.
(5) From a purse seine vessel or any
associated skiffs, other watercraft or
equipment, submerge lights under
water; suspend or hang lights over the
side of the purse seine vessel, skiff,
watercraft or equipment, or direct or use
lights in a manner other than as needed
to illuminate the deck of the purse seine
vessel or associated skiffs, watercraft or
equipment, to comply with navigational
requirements, and to ensure the health
and safety of the crew. These
prohibitions would not apply during
emergencies as needed to prevent
human injury or the loss of human life,
the loss of the purse seine vessel, skiffs,
watercraft or aircraft, or environmental
damage.
This proposed rule would revise the
introductory paragraph of 50 CFR
300.223(b)(1) to make it more clear that
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the prohibitions apply only to owners,
operators, and crew of purse seine
fishing vessels. NMFS has recently
received inquiries as to whether the
prohibitions apply to the owners,
operators, and crew of vessels using
other gear types. This proposed rule
would also make a technical change to
50 CFR 300.223(b)(1)(iv)(B) to clarify
that, during the FAD prohibition
periods, a FAD may be removed from
the water to be repaired, cleaned,
maintained, or otherwise serviced,
provided that it is not returned to the
water. This minor change ensures
consistency with the introductory
language in that paragraph.
NMFS has recently issued final
regulations to implement provisions of
a resolution adopted by the InterAmerican Tropical Tuna Commission
(IATTC) that includes restrictions on the
number of FADs with activated
instrumented buoys for each purse seine
vessel deployed at sea in the IATTC area
at any one time (see Final Rule; 83 FR
15503, published April 11, 2018). In
order to provide some consistency to the
regulated community, NMFS is
proposing similar regulations in this
rule to implement the limit regarding
FADs with activated instrumented
buoys specified in CMM 2017–01.
Under the proposed rule, an active
FAD is defined as a FAD that is
equipped with a buoy with a clearly
marked reference number allowing its
identification and equipped with a
satellite tracking system to monitor its
position, as specified by the definition
of instrumented buoy in CMM 2017–01.
CMM 2017–01 specifies that the buoy
shall be activated exclusively on board
the vessel. In order to implement this
provision, the proposed rule specifies
that the tracking equipment must be
turned on while the FAD is onboard the
vessel and before it is deployed in the
water. In accordance with CMM 2017–
01, under the proposed rule, each U.S.
purse seine vessel would have a limit of
350 active drifting FADs in the
Convention Area at any one time.
Purse Seine Fishing Effort Limits
In the past, NMFS has implemented
the U.S. purse seine fishing effort limits
on the high seas and in the U.S. EEZ
adopted by the Commission as a single
combined limit in a combined area of
the high seas and U.S. EEZ termed the
Effort Limit Area for Purse Seine or
ELAPS. NMFS’ reasoning for combining
the high seas and U.S. EEZ limits was
that it afforded more operational
flexibility to the fleet and there are no
substantial differences in terms of
effects to living marine resources for
treating the two areas separately or
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21751
combined so long as the overall effort
remained equal or less than the sum of
the two limits. For this proposed rule,
in light of CMM 2017–01’s provision
allowing the United States to transfer
some of its EEZ days to the high seas,
there is a need to separately account for
the U.S. high seas limit and the U.S.
EEZ limit. Thus, NMFS will no longer
combine the two limits under a single
limit. As stated above, CMM 2017–01
specifies a limit of 1,270 fishing days
per year for the high seas and a limit of
558 fishing days per year for the U.S.
EEZ. The proposed rule would establish
a limit of 1,370 fishing days on the high
seas and a separate limit of 458 fishing
days in the U.S. EEZ. These numbers
utilize the provision of CMM 2017–01
provided to alleviate the economic
hardship experienced by American
Samoa during a fishery closure and
transfer 100 fishing days from the U.S.
EEZ effort limit to the high seas effort
limit.
CMM 2017–01 also specifies that the
United States may add an additional
100 fishing days to its annual purse
seine fishing effort limit in the U.S. EEZ
if the limit in the U.S. EEZ is reached
by October 1, 2018. As discussed above,
NMFS is proposing to to implement the
elements of the rule so they are effective
until they are amended or replaced.
Thus, under the proposed rule, when
NMFS expects that the U.S. EEZ effort
limit would be reached by October 1,
NMFS would publish a notice in the
Federal Register, no later than seven
days prior to October 1, to increase the
U.S. EEZ effort limit by 100 fishing days
for that calendar year.
The meaning of ‘‘fishing day’’ is
defined at 50 CFR 300.211; that is, any
day in which a fishing vessel of the
United States equipped with purse seine
gear searches for fish, deploys a FAD,
services a FAD, or sets a purse seine,
with the exception of setting a purse
seine solely for the purpose of testing or
cleaning the gear and resulting in no
catch.
NMFS will monitor the number of
fishing days spent in the U.S. EEZ and
on the high seas using data submitted in
logbooks and other available
information. If and when NMFS
determines that a limit is expected to be
reached by a specific future date, it will
publish a notice in the Federal Register
announcing that the purse seine fishery
in the area where the limit is expected
to be reached will be closed starting on
a specific future date and will remain
closed until the end of the calendar
year. NMFS will publish that notice at
least seven days in advance of the
closure date. Starting on the announced
closure date, and for the remainder of
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calendar year, it will be prohibited for
U.S. purse seine vessels to fish in the
area where the limit is expected to be
reached, except that such vessels would
not be prohibited from bunkering
(refueling) during a fishery closure.
NMFS published an interim rule on
August 25, 2015 (see 80 FR 51478) to
remove the restriction that prohibited
U.S. purse seine vessels from
conducting bunkering during fishery
closures of the ELAPS. NMFS is
proposing to continue those regulations
as part of this proposed rule so that
bunkering would be allowed during any
fishery closures of the U.S. EEZ or high
seas due to reaching a limit in a given
calendar year.
Under existing regulations at 50 CFR
300.218(g), NMFS can direct U.S. purse
seine vessel owners and operators to
provide daily FAD reports, specifying
the number of purse seine sets made on
FADs during that day. NMFS
promulgated this regulation to help
track a limit on the number of FAD sets
that was applicable in previous years
but recognizes that this information is
also valuable to help predict when a
fishing effort limit is expected to be
reached with greater certainty. Thus,
under this proposed rule, NMFS would
revise the existing regulations so that
NMFS can direct U.S. purse seine vessel
owners and operators to provide reports
on the fishing activity of the vessel (e.g.,
setting, transiting, searching), location,
and type of set, in order to obtain better
data for tracking the fishing effort limits.
Eastern High Seas Special Management
Area
This proposed rule would remove the
requirements at 50 CFR 300.222(oo) and
50 CFR 300.225 for U.S. commercial
fishing vessels to provide reports prior
to entering or exiting the EHSSMA. This
proposed rule would also prohibit all
U.S. commercial fishing vessels fishing
for HMS from engaging in
transshipments in the EHSSMA,
beginning on January 1, 2019.
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Administrative Changes to Existing
Regulations
The regulations at 50 CFR 300.217(b)
and 300.218(a)(2)(v) contain outdated
cross references that would be corrected
by this proposed rule. In § 300.217,
paragraph (b)(1) would be revised to
provide a cross reference to
§ 300.336(b)(2), not § 300.14(b), and in
§ 300.218(a)(2)(v), the cross reference
would be to § 300.341(a) instead of to
§ 300.17(a) and (b). Sections 300.14(b)
and 300.17(a) and (b) no longer exist
and have been replaced through a new
regulatory action implementing
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provisions of the High Seas Fishing
Compliance Act (16 U.S.C. 5501 et seq.).
Classification
The Administrator, Pacific Islands
Region, NMFS, has determined that this
proposed rule is consistent with the
WCPFC Implementation Act and other
applicable laws, subject to further
consideration after public comment.
Section 304(b) of the MSA provides for
a 15 day comment period for these types
of fishery rules. Additionally, NMFS
finds ‘‘good cause’’ under the
Administrative Procedure Act that a
longer notice and comment period
would be contrary to the public interest.
5 U.S.C. 553(b)(B). As described above,
the first FAD prohibition period would
begin on July 1, 2018. Providing for
more than 15 days advance notice and
public comment on the proposed rule
increases the risk that the Commission’s
FAD prohibition period will become
effective prior to the effective date of the
final rule, possibly resulting in the
United States’ non-compliance with its
international obligations. Thus, in order
to provide the public with the
opportunity to comment on this
proposed rule while ensuring that the
agency has sufficient time to consider
any public comments and publish a
final rule that is effective by July 1,
2018, NMFS is providing the public
with a 15-day comment period on this
proposed rule.
the action, why it is being considered as
well as its objectives, and the legal basis
for this action are contained in the
SUMMARY section of the preamble and in
other sections of this SUPPLEMENTARY
INFORMATION section of the preamble.
The analysis follows:
Executive Order 12866
This proposed rule has been
determined to be not significant for
purposes of Executive Order 12866.
This proposed rule is not expected to be
an Executive Order 13771 regulatory
action because this proposed rule is not
significant under Executive Order
12866.
Estimated Number of Small Entities
Affected
For Regulatory Flexibility Act
purposes only, NMFS has established a
small business size standard for
businesses, including their affiliates,
whose primary industry is commercial
fishing (see 50 CFR 200.2). A business
primarily engaged in commercial fishing
(NAICS code 114111) is classified as a
small business if it is independently
owned and operated, is not dominant in
its field of operation (including its
affiliates), and has combined annual
receipts not in excess of $11 million for
all its affiliated operations worldwide.
The proposed rule would apply to
owners and operators of U.S.
commercial fishing vessels used to fish
for HMS in the Convention Area,
including longline vessels (except those
operating as part of the longline
fisheries of American Samoa, CNMI, or
Guam), purse seine vessels, and
albacore troll vessels. Based on the
number of U.S. vessels with WCPFC
Area Endorsements, which are required
to fish on the high seas in the
Convention Area, the estimated
numbers of affected longline, purse
seine, and albacore troll fishing vessels
is 163, 37, and 20, respectively.
Based on limited financial
information about the affected fishing
fleets, and using individual vessels as
proxies for individual businesses,
NMFS believes that all of the affected
longline and albacore troll vessels, and
slightly more than half of the vessels in
the purse seine fleet, are small entities
as defined by the RFA; that is, they are
independently owned and operated and
not dominant in their fields of
operation, and have annual receipts of
no more than $11.0 million. Within the
purse seine fleet, analysis of average
revenue, by vessel, for the three years of
2014–2016 reveals that average annual
revenue among vessels in the fleet was
about $10.2 million, and the three-year
annual averages were less than the $11
million threshold for 22 vessels in the
fleet.
Regulatory Flexibility Act (RFA)
An initial regulatory flexibility
analysis (IRFA) was prepared, as
required by section 603 of the RFA. The
IRFA describes the economic impact
this proposed rule, if adopted, would
have on small entities. A description of
Recordkeeping, Reporting, and Other
Compliance Requirements
The reporting, recordkeeping and
other compliance requirements of this
proposed rule are described earlier in
the preamble. The classes of small
entities subject to the requirements and
Coastal Zone Management Act (CZMA)
NMFS determined that this action is
consistent to the maximum extent
practicable with the enforceable policies
of the approved coastal management
program of American Samoa, the
Commonwealth of the Northern Mariana
Islands (CNMI), Guam, and the State of
Hawaii. Determinations to Hawaii and
each of the Territories were submitted
on March 12, 2018, for review by the
responsible state and territorial agencies
under section 307 of the CZMA.
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the types of professional skills necessary
to fulfill the requirements are described
below for each of the first four elements
of the proposed rule. The fifth element,
administrative changes to existing
regulations, is not considered further in
this IRFA because it would be of a
housekeeping nature and not have any
substantive effects on any entities.
1. Longline Bigeye Tuna Catch Limits
This element of the proposed rule
would not establish any new reporting
or recordkeeping requirements. The new
compliance requirement would be for
affected vessel owners and operators to
cease retaining, landing, and
transshipping bigeye tuna caught with
longline gear in the Convention Area if
and when the bigeye tuna catch limit of
3,554 mt (reduced by the amount of any
overages in the preceding year) is
reached in any of the years 2018–2020,
for the remainder of the calendar year,
subject to the exceptions and provisos
described in other sections of this
SUPPLEMENTARY INFORMATION section of
the preamble. Although the restrictions
that would come into effect in the event
the catch limit is reached would not
prohibit longline fishing, per se, they
are sometimes referred to in this
analysis as constituting a fishery
closure.
Fulfillment of this requirement is not
expected to require any professional
skills that the vessel owners and
operators do not already possess. The
costs of complying with this
requirement are described below to the
extent possible.
Complying with this element of the
proposed rule could cause foregone
fishing opportunities and result in
associated economic losses in the event
that the bigeye tuna catch limit is
reached in any of the years 2018–2020
and the restrictions on retaining,
landing, and transshipping bigeye tuna
are imposed for portions of those years.
These costs cannot be projected
quantitatively with any certainty. The
proposed annual limit of 3,554 mt can
be compared to catches in 2005–2008,
before limits were in place. The average
annual catch in that period was 4,709
mt. Based on that history, as well as
fishing patterns in 2009–2016, when
limits were in place, there appears to be
a relatively high likelihood of the
proposed limits being reached in 2018–
2020. In 2015, for example, which saw
exceptionally high catches of bigeye
tuna, the limit of 3,502 mt was
estimated to have been reached by, and
the fishery was closed on, August 5 (see
temporary rule published July 28, 2015;
80 FR 44883). The fishery was
subsequently re-opened for vessels
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included in agreements with the
governments of the CNMI and Guam
under regulations implementing
Amendment 7 to the Fishery Ecosystem
Plan for Pelagic Fisheries of the Western
Pacific Region (Pelagics FEP) (50 CFR
665.819). In 2016, the limit of 3,554 mt
was estimated to have been reached by
September 9, 2016, and in 2017, the
limit of 3,138 mt was estimated to have
been reached by September 1, 2017.
Thus, if bigeye tuna catch patterns in
2018–2020 are like those in 2005–2008,
the limit would be reached in the fourth
quarter of the year, and if they are like
those in 2015, 2016, or 2017, the limit
would be reached in the third quarter of
the year.
If the bigeye tuna limit is reached
before the end of any of the years 2018–
2020 and the Convention Area longline
bigeye tuna fishery is consequently
closed for the remainder of the calendar
year, it can be expected that affected
vessels would shift to the next most
profitable fishing opportunity (which
might be not fishing at all). Revenues
from that next best alternative activity
reflect the opportunity costs associated
with longline fishing for bigeye tuna in
the Convention Area. The economic cost
of the proposed rule would not be the
direct losses in revenues that would
result from not being able to fish for
bigeye tuna in the Convention Area, but
rather the difference in benefits derived
from that activity and those derived
from the next best activity. The
economic cost of the proposed rule on
affected entities is examined here by
first estimating the direct losses in
revenues that would result from not
being able to fish for bigeye tuna in the
Convention Area as a result of the catch
limit being reached. Those losses
represent the upper bound of the
economic cost of the proposed rule on
affected entities. Potential next-best
alternative activities that affected
entities could undertake are then
identified in order to provide a (mostly
qualitative) description of the degree to
which actual costs would be lower than
that upper bound.
Upper bounds on potential economic
costs can be estimated by examining the
projected value of longline landings
from the Convention Area that would
not be made as a result of reaching the
limit. For this purpose, it is assumed
that, absent this proposed rule, bigeye
tuna catches in the Convention Area in
each of the years 2018–2020 would be
5,000 mt, slightly more than the average
in 2005–2008. Under this scenario,
imposition of annual limits of 3,554 mt
would result in 29 percent less bigeye
tuna being caught each year than under
no action. In the deep-set fishery,
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catches of marketable species other than
bigeye tuna would likely be affected in
a similar way if vessels do not shift to
alternative activities. Assuming for the
moment that ex-vessel prices would not
be affected by a fishery closure, under
the proposed rule, revenues in 2018–
2020 to entities that participate
exclusively in the deep-set fishery
would be approximately 29 percent less
than under no action. Average annual
ex-vessel revenues (from all species) per
mt of bigeye tuna caught during 2005–
2008 were about $14,190/mt (in 2014
dollars, derived from the latest available
annual report on the pelagic fisheries of
the western Pacific Region (Western
Pacific Regional Fishery Management
Council, 2014, Pelagic Fisheries of the
Western Pacific Region: 2012 Annual
Report. Honolulu, Western Pacific
Fishery Management Council)). If there
are 128 active vessels in the fleet, as
there were during 2005–2008, on
average, then under the no-action
scenario of fleet-wide anual catches of
5,000 mt, each vessel would catch 39
mt/yr, on average. Reductions of 29
percent in 2018–2020 as a result of the
proposed limits would be about 11 mt
per year. Applying the average ex-vessel
revenues (from all species) of $14,190
per mt of bigeye tuna caught, the
reductions in ex-vessel revenue per
vessel would be $160,000 per year, on
average.
In the shallow-set fishery, affected
entities would bear limited costs in the
event of the limit being reached (but
most affected entities also participate in
the deep-set fishery and might bear
costs in that fishery, as described
below). The cost would be about equal
to the revenues lost from not being able
to retain or land bigeye tuna captured
while shallow-setting in the Convention
Area, or the cost of shifting to shallowsetting in the eastern Pacific Ocean
(EPO), which is to the east of 150
degrees W longitude, whichever is less.
In the fourth calendar quarters of 2005–
2008, almost all shallow-setting effort
took place in the EPO, and 97 percent
of bigeye tuna catches were made there,
so the cost of a bigeye tuna fishery
closure to shallow-setting vessels would
appear to be very limited. During 2005–
2008, the shallow-set fishery caught an
average of 54 mt of bigeye tuna per year
from the Convention Area. If the
proposed bigeye tuna catch limit is
reached even as early as July 31 in any
of the years 2018–2020, the Convention
Area shallow-set fishery would have
caught at that point, based on 2005–
2008 data, on average, 99 percent of its
average annual bigeye tuna catches.
Imposition of the landings restriction at
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that point in any of the years 2018–2020
would result in the loss of revenues
from approximately 0.5 mt (1 percent of
54 mt) of bigeye tuna, which, based on
recent ex-vessel prices, would be worth
no more than $5,000. Thus, expecting
about 27 vessels to engage in the
shallow-set fishery (the annual average
in 2005–2012), the average of those
potentially lost annual revenues would
be no more than $200 per vessel. The
remainder of this analysis focuses on
the potential costs of compliance in the
deep-set fishery.
It should be noted that the impacts on
affected entities’ profits would be less
than impacts on revenues when
considering the costs of operating
vessels, because costs would be lower if
a vessel ceases fishing after the catch
limit is reached. Variable costs can be
expected to be affected roughly in
proportion to revenues, as both variable
costs and revenues would stop accruing
once a vessel stops fishing. But affected
entities’ costs also include fixed costs,
which are borne regardless of whether a
vessel is used to fish—e.g., if it is tied
up at the dock during a fishery closure.
Thus, profits would likely be adversely
impacted proportionately more than
revenues.
As stated previously, actual
compliance costs for a given entity
might be less than the upper bounds
described above, because ceasing fishing
would not necessarily be the most
profitable alternative opportunity when
the catch limit is reached. Two
alternative opportunities that are
expected to be attractive to affected
entities include: (1) Deep-set longline
fishing for bigeye tuna in the
Convention Area in a manner such that
the vessel is considered part of the
longline fishery of American Samoa,
Guam, or the CNMI; and (2) deep-set
longline fishing for bigeye tuna and
other species in the EPO. These two
opportunities are discussed in detail
below. Four additional opportunities
are: (3) Shallow-set longline fishing for
swordfish (for deep-setting vessels that
would not otherwise do so), (4) deep-set
longline fishing in the Convention Area
for species other than bigeye tuna, (5)
working in cooperation with vessels
operating as part of the longline
fisheries of the Participating
Territories—specifically, receiving
transshipments at sea from them and
delivering the fish to the Hawaii market,
and (6) vessel repair and maintenance.
A study by NMFS of the effects of the
WCPO bigeye tuna longline fishery
closure in 2010 (Richmond, L., D.
Kotowicz, J. Hospital and S. Allen,
2015, Monitoring socioeconomic
impacts of Hawai‘i’s 2010 bigeye tuna
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closure: Complexities of local
management in a global fishery, Ocean
& Coastal Management 106:87–96) did
not identify the occurrence of any
alternative activities that vessels
engaged in during the closure, other
than deep-setting for bigeye tuna in the
EPO, vessel maintenance and repairs,
and granting lengthy vacations to
employees. Based on those findings,
NMFS expects that alternative
opportunities (3), (4), (5) and (6) are
probably unattractive relative to the first
two alternatives, and are not discussed
here in any further detail. NMFS
recognizes that vessel maintenance and
repairs and granting lengthy vacations
to employees are two alternative
activities that might be taken advantage
of if the fishery is closed, but no further
analysis of their mitigating effects is
provided here.
Before examining in detail the two
potential alternative fishing
opportunities that would appear to be
the most attractive to affected entities, it
is important to note that under the
proposed rule, once the limit is reached
and the WCPO bigeye tuna fishery is
closed, fishing with longline gear both
inside and outside the Convention Area
during the same trip would be
prohibited (except in the case of a
fishing trip that is in progress when the
limit is reached and the restrictions go
into effect). For example, after the
restrictions go into effect, during a given
fishing trip, a vessel could be used for
longline fishing for bigeye tuna in the
EPO or for longline fishing for species
other than bigeye tuna in the
Convention Area, but not for both. This
reduced operational flexibility would
bring costs, because it would constrain
the potential profits from alternative
opportunities. Those costs cannot be
quantified.
A vessel could take advantage of the
first alternative opportunity (deepsetting for bigeye tuna in a manner such
that the vessel is considered part of the
longline fishery of one of the three U.S.
Participating Territories), by three
possible methods: (a) Landing the
bigeye tuna in one of the three
Participating Territories, (b) holding an
American Samoa Longline Limited
Access Permit, or (c) being considered
part of a Participating Territory’s
longline fishery, by agreement with one
or more of the three Participating
Territories under the regulations
implementing Amendment 7 to the
Pelagics FEP (50 CFR 665.819). In the
first two circumstances, the vessel
would be considered part of the longline
fishery of the Participating Territory
only if the bigeye tuna were not caught
in the portion of the U.S. EEZ around
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Sfmt 4702
the Hawaiian Islands and were landed
by a U.S. vessel operating in compliance
with a permit issued under the
regulations implementing the Pelagics
FEP or the Fishery Management Plan for
U.S. West Coast Fisheries for Highly
Migratory Species.
With respect to the first method of
engaging in alternative opportunity 1
(1.a.) (landing the bigeye tuna in one of
the Participating Territories), there are
three potentially important constraints.
First, whether the fish are landed by the
vessel that caught the fish or by a vessel
to which the fish were transshipped, the
costs of a vessel transiting from the
traditional fishing grounds in the
vicinity of the Hawaiian Archipelago to
one of the Participating Territories
would be substantial. Second, none of
these three locales has large local
consumer markets to absorb substantial
additional landings of fresh sashimigrade bigeye tuna. Third, transporting
the bigeye tuna from these locales to
larger markets, such as markets in
Hawaii, the U.S. west coast, or Japan,
would bring substantial additional costs
and risks. These cost constraints suggest
that this alternative opportunity has
limited potential to mitigate the
economic impacts of the proposed rule
on affected small entities.
The second method of engaging in the
first alternative opportunity (1.b.)
(having an American Samoa Longline
Limited Access Permit), would be
available only to the subset of the
Hawaii longline fleet that has both
Hawaii and American Samoa longline
permits (dual permit vessels). Vessels
that do not have both permits could
obtain them if they meet the eligibility
requirements and pay the required
costs. For example, the number of dual
permit vessels increased from 12 in
2009, when the first WCPO bigeye tuna
catch limit was established, to 23 in
2016. The previously cited NMFS study
of the 2010 fishery closure (Richmond et
al. 2015) found that bigeye tuna
landings of dual permit vessels
increased substantially after the start of
the closure on November 22, 2010,
indicating that this was an attractive
opportunity for dual permit vessels, and
suggesting that those entities might have
benefitted from the catch limit and the
closure.
The third method of engaging in the
first alternative opportunity (1.c.)
(entering into an Amendment 7
agreement), was also available in 2011–
2017 (in 2011–2013, under section
113(a) of Public Law 112–55, 125 Stat.
552 et seq., the Consolidated and
Further Continuing Appropriations Act,
2012, continued by Public Law 113–6,
125 Stat. 603, section 110, the
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Department of Commerce
Appropriations Act, 2013; hereafter,
‘‘section 113(a)’’). As a result of
agreements that were in place in 2011–
2014, the WCPO bigeye tuna fishery was
not closed in any of those years. In
2015, 2016, and 2017 the fishery was
closed but then reopened when
agreements went into effect.
Participation in an Amendment 7
agreement would likely not come
without costs to fishing businesses. As
an indication of the possible cost, the
terms of the agreement between
American Samoa and the members of
the Hawaii Longline Association (HLA)
in effect in 2011 and 2012 included
payments totaling $250,000 from the
HLA to the Western Pacific Sustainable
Fisheries Fund, equal to $2,000 per
vessel. It is not known how the total
cost was allocated among the members
of the HLA, so it is possible that the
owners of particular vessels paid
substantially more than or less than
$2,000.
The second alternative opportunity
(2) (deep-set fishing for bigeye tuna in
the EPO), would be an option for
affected entities only if it is allowed
under regulations implementing the
decisions of the IATTC. NMFS has
issued a final rule to implement the
IATTC’s most recent resolution on the
management of tropical tuna stocks (83
FR 15503; April 11, 2018). The final rule
establishes an annual limit of 750 mt on
the catch of bigeye tuna in the EPO by
vessels at least 24m in length in each of
the years 2018–2020. Annual longline
bigeye tuna catch limits have been in
place for the EPO in most years since
2004. Since 2009, when the limit was
500 mt, it was reached in 2013
(November 11), 2014 (October 31), and
2015 (August 12). In 2016 NMFS
forecasted that the limit would be
reached July 25 and subsequently closed
the fishery, but later determined that the
catch limit had not been reached and reopened the fishery on October 4, 2016
(81 FR 69717). The limit was not
reached in 2017.
The highly seasonal nature of bigeye
tuna catches in the EPO and the
relatively high inter-annual variation in
catches prevents NMFS from making a
useful prediction of whether and when
the EPO limits in 2018–2020 are likely
to be reached. If it is reached, this
alternative opportunity would not be
available for large longline vessels,
which constitute about a quarter of the
fleet.
Historical fishing patterns can provide
an indication of the likelihood of
affected entities making use of the
opportunity of deep-setting in the EPO
in the event of a closure in the WCPO.
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The proportion of the U.S. fishery’s
annual bigeye tuna catches that were
captured in the EPO from 2005 through
2008 ranged from 2 percent to 22
percent, and averaged 11 percent. In
2005–2007, that proportion ranged from
2 percent to 11 percent, and may have
been constrained by the IATTC-adoped
bigeye tuna catch limits established by
NMFS (no limit was in place for 2008).
Prior to 2009, most of the U.S. annual
bigeye tuna catch by longline vessels in
the EPO typically was made in the
second and third quarters of the year; in
2005–2008 the percentages caught in the
first, second, third, and fourth quarters
were 14, 33, 50, and 3 percent,
respectively. These data demonstrate
two historical patterns—that relatively
little of the bigeye tuna catch in the
longline fishery was typically taken in
the EPO (11 percent in 2005–2008, on
average), and that most EPO bigeye tuna
catches were made in the second and
third quarters, with relatively few
catches in the fourth quarter when the
proposed catch limit would most likely
be reached. These two patterns suggest
that there could be substantial costs for
at least some affected entities that shift
to deep-set fishing in the EPO in the
event of a closure in the WCPO. On the
other hand, fishing patterns since 2008
suggest that a substantial shift in deepset fishing effort to the EPO could occur.
In 2009, 2010, 2011, 2012, 2013, 2014,
2015, and 2016 the proportions of the
fishery’s annual bigeye tuna catches that
were captured in the EPO were about
16, 27, 23, 19, 36, 35, 47, and 36
percent, respectively, and most bigeye
tuna catches in the EPO were made in
the latter half of the calendar years.
The NMFS study of the 2010 closure
(Richmond et al. 2015) found that some
businesses—particularly those with
smaller vessels—were less inclined than
others to fish in the EPO during the
closure because of the relatively long
distances that would need to be
travelled in the relatively rough winter
ocean conditions. The study identified a
number of factors that likely made
fishing in the EPO less lucrative than
fishing in the WCPO during that part of
the year, including fuel costs and the
need to limit trip length in order to
maintain fish quality and because of
limited fuel storage capacity.
In addition to affecting the volume of
landings of bigeye tuna and other
species, the proposed catch limits could
affect fish prices, particularly during a
fishery closure. Both increases and
decreases appear possible. After a limit
is reached and landings from the WCPO
are prohibited, ex-vessel prices of bigeye
tuna (e.g., that are caught in the EPO or
by vessels in the longline fisheries of the
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21755
three U.S. Participating Territories), as
well as of other species landed by the
fleet, could increase as a result of the
constricted supply. This would mitigate
economic losses for vessels that are able
to continue fishing and landing bigeye
tuna during the closure. For example,
the NMFS study of the 2010 closure
(Richmond et al. 2015) found that exvessel prices during the closure in
December were 50 percent greater than
the average during the previous five
Decembers. (It is emphasized that
because it was an observational study,
neither this nor other observations of
what occurred during the closure can be
affirmatively linked as effects of the
fishery closure.)
Conversely, a WCPO bigeye tuna
fishery closure could cause a decrease
in ex-vessel prices of bigeye tuna and
other products landed by affected
entities if the interruption in the local
supply prompts the Hawaii market to
shift to alternative (e.g., imported)
sources of bigeye tuna. Such a shift
could be temporary—that is, limited to
2018–2020—or it could lead to a more
permanent change in the market (e.g., as
a result of wholesale and retail buyers
wanting to mitigate the uncertainty in
the continuity of supply from the
Hawaii longline fisheries). In the latter
case, if locally caught bigeye tuna
fetches lower prices because of stiffer
competition with imported bigeye tuna,
then ex-vessel prices of local product
could be depressed indefinitely. The
NMFS study of the 2010 closure
(Richmond et al. 2015) found that a
common concern in the Hawaii fishing
community prior to the closure in
November 2010 was retailers having to
rely more heavily on imported tuna,
causing imports to gain a greater market
share in local markets. The study found
this not to have been borne out, at least
not in 2010, when the evidence gathered
in the study suggested that few buyers
adapted to the closure by increasing
their reliance on imports, and no reports
or indications were found of a dramatic
increase in the use of imported bigeye
tuna during the closure. The study
concluded, however, that the 2010
closure caused buyers to give increased
consideration to imports as part of their
business model, and it was predicted
that tuna imports could increase during
any future closure. To the extent that exvessel prices would be reduced by this
action, revenues earned by affected
entities would be affected accordingly,
and these impacts could occur both
before and after the limit is reached, and
as described above, possibly after 2020.
The potential economic effects
identified above would vary among
individual business entities, but it is not
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possible to predict the range of
variation. Furthermore, the impacts on a
particular entity would depend on both
that entity’s response to the proposed
rule and the behavior of other vessels in
the fleet, both before and after the catch
limit is reached. For example, the
greater the number of vessels that take
advantage—before the limit is reached—
of the first alternative opportunity (1),
fishing as part of one of the Participating
Territory’s fisheries, the lower the
likelihood that the limit would be
reached.
The fleet’s behavior in 2011 and 2012
is illustrative. In both those years, most
vessels in the Hawaii fleet were
included in a section 113(a)
arrangement with the government of
American Samoa, and as a consequence,
the U.S. longline catch limit was not
reached in either year. Thus, none of the
vessels in the fleet, including those not
included in the section 113(a)
arrangements, were prohibited from
fishing for bigeye tuna in the
Convention Area at any time during
those two years. The fleet’s experience
in 2010 (before opportunities under
section 113(a) or Amendment 7 to the
Pelagics FEP were available) provides
another example of how economic
impacts could be distributed among
different entities. In 2010 the limit was
reached and the WCPO bigeye tuna
fishery was closed on November 22. As
described above, dual permit vessels
were able to continue fishing outside
the U.S. EEZ around the Hawaiian
Archipelago and benefit from the
relatively high ex-vessel prices that
bigeye tuna fetched during the closure.
In summary, based on potential
reductions in ex-vessel revenues, NMFS
has estimated that the upper bound of
potential economic impacts of the
proposed rule on affected longline
fishing entities could be roughly
$160,000 per vessel per year, on
average. The actual impacts to most
entities are likely to be substantially less
than those upper bounds, and for some
entities the impacts could be neutral or
positive (e.g., if one or more
Amendment 7 agreements are in place
in 2018–2020 and the terms of the
agreements are such that the U.S.
longline fleet is effectively
unconstrained by the catch limits).
2. FAD Restrictions
This element of the proposed rule
would not establish any new reporting
or recordkeeping requirements. The new
requirement would be for affected vessel
owners and operators to comply with
the FAD restrictions described earlier in
the SUPPLEMENTARY INFORMATION section
of the preamble, including FAD
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prohibition periods throughout the
Convention Area from July 1 through
September 30 in each of the years 2018–
2020 and FAD prohibition periods just
on the high seas in the Convention Area
from November 1 through December 31
in each of the same years. There would
also be a limit of 350 active FADs that
may be deployed per vessel at any given
time. Anecdotal information from the
U.S. purse seine fishing industry
indicates that U.S. purse seine vessels
have not ever deployed more than 350
active FADs at any given time, so NMFS
does not expect that the limit would be
constraining or otherwise affect the
behavior of purse seine operations, and
it is not considered further in this IRFA.
Fulfillment of the element’s
requirements is not expected to require
any professional skills that the vessel
owners and operators do not already
possess. The costs of complying with
the requirements are described below to
the extent possible.
The proposed FAD restrictions would
substantially constrain the manner in
which purse seine fishing could be
conducted in the specified areas and
periods in the Convention Area; in those
areas and during those periods, vessels
would be able to set only on free, or
‘‘unassociated,’’ schools.
With respect to the three-month FAD
closure throughout the Convention
Area: Assuming that sets would be
evenly distributed through the year, the
number of annual FAD sets would be
expected to be about three-fourths the
number that would occur without a
seasonal FAD closure. For example,
during 2014–2016, the proportion of all
sets that were made on FADs when FAD
setting was allowed was 50 percent. As
an indicative example, if the fleet makes
8,000 sets in a given year (somewhat
more than the 2014–2016 average of
7,420 sets per year) and 50 percent of
those are FAD sets, it would make 4,000
FAD sets. If there is a three-month
closure and 50 percent of the sets
outside the closure are FAD sets, and
sets are evenly distributed throughout
each year, the annual number of FAD
sets would be 3,000. This can be
compared to the estimated 2,494 annual
FAD sets that were made in 2014–2016,
on average, when there were threemonth FAD closures.
With respect to the two-month high
seas FAD closure: The effects of this
element are difficult to predict. If the
high seas are closed to all purse seine
fishing during November–December as a
result of the fishing effort limit being
reached, the high seas FAD closure
during those two months would have no
additional effect whatsoever. If the high
seas are not closed to fishing, the
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prohibition on FAD setting would make
the high seas less favorable for fishing
than they otherwise would be, because
only unassociated sets would be
allowed there. It is not possible to
characterize how influential that factor
would be, however. Thus, it is not
possible to predict the effects in terms
of the spatial distribution of fishing
effort or the proportion of fishing effort
that is made on FADs.
With respect to both the three-month
FAD closure and two-month high seas
FAD closure: As for the limits on fishing
effort, vessel operators might choose to
schedule their routine maintenance
periods so as to take best advantage of
the available opportunities for making
FAD sets, such as during the FAD
closures. However, the limited number
of vessel maintenance facilities in the
region might constrain vessel operators’
ability to do this.
It is emphasized that the indicative
example given above is based on the
assumption that the FAD set ratio would
be 50 percent during periods when FAD
sets are allowed, as well as that sets are
distributed evenly throughout the year.
These assumptions are weak from
several perspectives, so the results
should be interpreted with caution.
First, as described above, FAD set ratios
have varied widely from year to year,
indicating that the conditions that
dictate ‘‘optimal’’ FAD set ratios for the
fleet vary widely from year to year, and
cannot be predicted with any certainty.
Second, the optimal FAD set ratio
during open periods might depend on
how long and when those periods occur.
For example, FAD fishing might be
particularly attractive soon after a
closed period during which FADs
aggregated fish but were not fished on.
These factors are not explicitly
accounted for in this analysis, but the 50
percent FAD ratio used in this analysis
was taken from 2014–2016, when there
was a three-month FAD closure, so it is
probably a better indicator for the action
alternatives than FAD set ratios for years
prior to 2009, when no seasonal FAD
closures were in place. With respect to
the distribution of sets through the year,
the existence of collective limits on
fishing effort might create an incentive
for individual vessels to fish harder
earlier in the year than they otherwise
would, resulting in a ‘‘race to fish.’’
Limitations on fishing effort throughout
the Convention Area could cause
vessels to fish (irrespective of set type
or the timing of FAD closures) harder
earlier in a given year than they would
without the limits. However, any such
effect is not expected to be great,
because most vessels in the fleet tend to
fish virtually full time, leaving little
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flexibility to increase fishing effort at
any particular time of the year.
Vessels in the U.S. WCPO purse seine
fleet make both unassociated sets and
FAD sets when not constrained by
regulation, so one type of set is not
always more valuable or efficient than
the other type. Which set type is
optimal at any given time is a function
of immediate conditions in and on the
water, but probably also of such factors
as fuel prices (unassociated sets involve
more searching time and thus tend to
bring higher fuel costs than FAD sets)
and market conditions (e.g., FAD
fishing, which tends to result in greater
catches of lower-value skipjack tuna and
smaller yellowfin tuna and bigeye tuna
than unassociated sets, might be more
attractive and profitable when canneries
are not rejecting small fish). Clearly, the
ability to do either type of set is
valuable, and constraints on the use of
either type can be expected to bring
adverse economic impacts to fishing
operations. Thus, the greater the
constraints on the ability to make FAD
sets, the greater the expected economic
impacts of the action. Because the
factors affecting the relative value of
FAD sets and unassociated sets are
many, and the relationships among
them are not well known, it is not
possible to quantify the expected
economic impacts of the FAD
restrictions. However, it appears
reasonable to conclude the following:
First, the FAD restrictions would
adversely impact producer surplus
relative to the no-action alternative. The
fact that the fleet has made such a
substantial portion of its sets on FADs
in the past indicates that prohibiting the
use of FADs in the specified areas and
periods could bring substantial costs
and/or revenue losses. Second, vessel
operators might be able to mitigate the
impacts of the FAD restrictions by
scheduling their routine vessel and
equipment maintenance during the FAD
closures, but this opportunity might be
constrained by the limited vessel
maintenance facilities in the region.
3. Purse Seine Fishing Effort Limits
This element of the proposed rule
would not establish any new reporting
or recordkeeping requirements, but the
existing ‘‘Daily FAD reports’’ required at
50 CFR 300.218(g) would be slightly
revised, and renamed ‘‘Daily purse seine
fishing effort reports’’ and would
slightly modify the type of information
collected.
There would be annual limits of 1,370
and 458 fishing days on the high seas
and in the U.S. EEZ, respectively, in the
Convention Area. In addition, there
would be a mechanism to increase the
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U.S. EEZ limit in a given year to 558
fishing days if 458 fishing days are used
by October 1 of that year.
Fulfillment of this element’s
requirements is not expected to require
any professional skills that the vessel
owners and operators do not already
possess. The costs of complying with
the requirements are described below to
the extent possible.
Regarding the modification to the
daily reporting requirement, the specific
information required in the reports
would be slightly modified from those
of the existing ‘‘Daily FAD reports,’’ but
the costs of compliance are not expected
to change.
Regarding the fishing effort limits, if
and when the fishery on the high seas
or in the U.S. EEZ is closed as a result
of a limit being reached in any of the
years 2018–2020, owners and operators
of U.S. purse seine vessels would have
to cease fishing in that area for the
remainder of the calendar year. Closure
of the fishery in either of those areas
could thereby cause foregone fishing
opportunities and associated economic
losses if the area contains preferred
fishing grounds during such a closure.
Historical fishing rates in the two areas
give a rough indication of the likelihood
of the limits being reached.
Regarding the U.S. EEZ, from 2009
through 2017 (NMFS has only
preliminary estimates for 2017), no
more than 50 percent of the proposed
limit of 458 fishing days was ever used
(and no more than the 41 percent of the
possible limit of 558 fishing days). This
history suggests a relatively low
likelihood of the proposed EEZ limit
being reached in 2018–2020. However,
the allowance for an extra 100 fishing
days if the 458 fishing days are used by
October 1 could provide an incentive for
the fleet to use more fishing days in the
EEZ than it otherwise would.
Furthermore, this would be the first
time that separate limits would be
established for the EEZ and the high
seas, so the incentives for individual
vessels in the fleet would change. A
minority of the fleet is authorized to fish
in the U.S. EEZ (8 of the 33 vessels
currently licensed under the South
Pacific Tuna Treaty (SPTT) 1 have
fishery endorsements on their U.S.
Coast Guard Certificates of
Documentation, which are required to
fish in the U.S. EEZ, and 1 of the other
4 purse seine vessels with WCPFC Area
Endorsements has a fishery
endorsement), and with a separate limit
1 The majority of U.S. purse seine fishing activity
in the Convention Area takes place in the waters of
Pacific Island Parties to the SPTT (PIPs), pursuant
to the terms of the SPTT.
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21757
for the U.S. EEZ, this minority might
take more advantage of it than it has in
the past.
Regarding the high seas from 2009
through 2017, between 31 and 135
percent of the proposed limit of 1,370
fishing days was used, and at least 100
percent was used in three of the nine
years. In two years, 2015 and 2016, the
ELAPS was closed for part of the year
(starting June 15 in 2015, and September
2 in 2016), so more fishing effort might
have occurred in those two years were
there no limits. This history suggests a
substantial likelihood of the proposed
high seas limit being reached in any of
the years 2018–2020.
Two factors could have a substantial
influence on the amount of fishing effort
in the U.S. EEZ and on the high seas in
2018–2020: First, the number of fishing
days available in foreign waters (the
fleet’s main fishing grounds) pursuant to
the SPTT will influence the incentive to
fish outside those waters, including the
U.S. EEZ and high seas. Second, El
˜
Nino—Southern Oscillation (ENSO)
conditions will influence where the best
fishing grounds are.
Regarding fishing opportunities in
foreign waters, in December 2016, the
United States and PIPs agreed upon a
revised SPTT, and under this new
agreement U.S. purse seine fishing
businesses can purchase fishing days in
the EEZs of the PIPs. There are limits on
the number of such ‘‘upfront’’ fishing
days that may be purchased. These
limits can influence the amount of
fishing in other areas, such as the U.S.
EEZ and the high seas, as well as the
EPO. For example, if the number of
available upfront fishing days is
relatively small, fishing effort in the
U.S. EEZ and/or high seas might be
relatively great. In fact, the number of
upfront days available for the Kiribati
EEZ, which has traditionally constituted
important fishing grounds for the U.S.
fleet, is notably small—only 300 fishing
days per year. However, the new SPTT
regime provides for U.S. purse seine
fishing businesses to purchase
‘‘additional’’ fishing days through direct
bilateral agreements with the PIPs.
NMFS cannot project how many
additional days will be purchased in
any given years, so cannot gauge how
the limits on upfront days might
influence fishing effort in the U.S. EEZ
or on the high seas. Limits on upfront
days are therefore not considered here
any further.
Additionally, effective January 1,
2015, Kiribati prohibited commercial
fishing in the Phoenix Islands Protected
Area, which is a large portion of the
Kiribati EEZ around the Phoenix
Islands. These limitations in the Kiribati
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EEZ in 2015 probably made fishing in
the ELAPS more attractive than it
otherwise would be.
˜
Regarding El Nino Southern
Oscillation (ENSO) conditions, the
eastern areas of the WCPO tend to be
comparatively more attractive to the
˜
U.S. purse seine fleet during El Nino
events, when warm surface water
spreads from the western Pacific to the
eastern Pacific and large, valuable
yellowfin tuna become more vulnerable
to purse seine fishing and trade winds
lessen in intensity. Consequently, the
U.S. EEZ and high seas, much of which
is situated in the eastern range of the
fleet’s fishing grounds, is likely to be
more important fishing grounds to the
˜
fleet during El Nino events (as
˜
compared to neutral or La Nina events).
This is supported by there being a
statistically significant correlation
between annual average per-vessel
fishing effort in the ELAPS and the
˜
Oceanic Nino Index, a common measure
of ENSO conditions, over the life of the
SPTT through 2010.
˜
El Nino conditions were present in
2015 and in the first half of 2016, and
might have contributed to the relatively
high rates of fishing in the ELAPS in
those years. ENSO neutral conditions
began in the latter half of 2016, and
continued until the fourth quarter of
˜
2017, when there was a shift to La Nina
conditions, which persisted through
early 2018 (and which is consistent with
the moderate rates of fishing in the
ELAPS in 2017). As of February 8, 2018,
the National Weather Service states that
˜
a transition from La Nino to ENSOneutral conditions is likely (∼55 percent
chance) in March–May of 2018 (NWS
2018). Thus ENSO conditions might
have a negative influence on fishing in
the U.S. EEZ and the high seas early in
2018 and a largely neutral influence for
the rest of 2018. Their influence on
fishing effort in 2019 and 2020 cannot
be predicted with any certainty.
Another potentially important factor
is that the EEZ and high seas limits
would be competitive limits, so their
establishment could cause a ‘‘race to
fish’’ in the two areas. That is, vessel
operators might seek to take advantage
of the limited number of fishing days
available in the areas before the limits
are reached, and fish harder in the
ELAPS than they would if there were no
limits. On the one hand, any such raceto-fish effect might be reflected in the
history of fishing in the ELAPS,
described above. On the other hand,
anecdotal information from the fishing
industry suggests that the limits might
have been internally allocated by the
fleet, which might have tempered any
race to fish. It is not known whether the
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industry intends to internally allocate
the proposed limits.
In summary, although difficult to
predict, either the U.S. EEZ or high seas
limits could be reached in any of the
years 2018–2020, especially the high
seas limits. If either limit is reached in
a given year, the fleet would be
prohibited from fishing in that area for
the remainder of the calendar year.
The closure of any fishing grounds for
any amount of time can be expected to
bring adverse impacts to affected
entities (e.g., because the open area
might, during the closed period, be less
productive than the closed area, and
vessels might use more fuel and spend
more time having to travel to open
areas). The severity of the impacts of a
closure would depend greatly on the
length of the closure and where the
most favored fishing grounds are during
the closure. A study by NMFS (Chan, V.
and D. Squires. 2016. Analyzing the
economic impacts of the 2015 ELAPS
closure. NMFS Internal Report)
estimated that the overall losses to the
combined sectors of the vessels,
canneries and vessel support companies
from the 2015 ELAPS closure ranged
from $11 million and $110 million
depending on the counterfactual period
considered. These results suggest that
there were impacts from the ELAPS
closure on the American Samoa
economy and a connection between U.S.
purse seine vessels and the broader
American Samoa economy.
If either the U.S. EEZ or high seas is
closed, possible next-best opportunities
for U.S. purse seine vessels fishing in
the WCPO include fishing in the other
of the two areas, fishing in foreign EEZs
inside the Convention Area, fishing
outside the Convention Area in EPO,
and not fishing.
With respect to fishing in the U.S.
EEZ or on the high seas: If the U.S. EEZ
were closed, the high seas would be
available to the fleet until its limit is
reached. If the high seas were closed,
the U.S. EEZ would be available until its
limit is reached, but only for the vessels
with fishery endorsements on their
Certificates of Documentation (currently
9, including 8 vessels with SPTT
licenses and one additional vessel
without).
With respect to fishing in the
Convention Area in foreign EEZs: As
described above, under the SPTT the
fleet might have substantial fishing days
available in the Pacific Island country
EEZs that dominate the WCPO, but it is
not possible to predict how many
fishing days will be available to the fleet
as a whole or to individual fishing
businesses.
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With respect to fishing in the EPO:
The fleet has generally increased its
fishing operations in the EPO since
2014, and as of 2017, there were 17
purse seine vessel in the WCPO fleet
that are also listed on the IATTC Vessel
Register. In order to fish in the EPO, a
vessel must be on the IATTC’s Regional
Vessel Register and categorized as active
(50 CFR 300.22(b)), which involves fees
of about $14.95 per cubic meter of well
space per year (e.g., a vessel with 1,200
m3 of well space would be subject to
annual fees of $17,940). (As an
exception to this rule, an SPTT-licensed
vessel is allowed to make one fishing
trip in the EPO each year without being
categorized as active on the IATTC
Regional Vessel Register. The trip must
not exceed 90 days in length, and there
is an annual limit of 32 such trips for
the entire SPTT-licensed fleet (50 CFR
300.22(b)(1)).) The number of U.S. purse
seine vessels in the WCPO fleet that
have opted to be categorized as such has
increased in the last few years from zero
to 17, probably largely a result of
constraints on fishing days in the WCPO
and/or uncertainty in future access
arrangements under the SPTT. This
suggests an increasing attractiveness of
fishing in the EPO, in spite of the costs
associated with doing so. However, in
2018 vessels probably will not have the
opportunity to fish in the EPO yearround. To implement a recent decision
of the IATTC, NMFS has published a
final rule that requires purse seine
vessels to choose between two EPO
fishing prohibition periods each year in
2018–2020: July 29–October 8 or
November 9–January 19 (72 days in
either case). Thus, the opportunity to
fish in the EPO might be constrained,
depending on when the U.S. EEZ and/
or high seas in the WCPFC Area is
closed, and which EPO closure period a
given vessel operator chooses.
With respect to not fishing at all
during a closure of the U.S. EEZ or high
seas: This would mean a loss of any
revenues from fishing. However, many
of the vessels’ variable operating costs
would be avoided in that case, and it is
possible that for some vessels a portion
of the time might be used for productive
activities like vessel and equipment
maintenance.
The opportunity costs of engaging in
next-best opportunities in the event of a
closure are not known, so the potential
impacts cannot be quantified. However,
to give an indication of the magnitude
of possible economic impacts to
producers in the fishery (i.e., an
indication of the upper bound of those
impacts), information on revenues per
day is provided here.
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The last five years for which catch
estimates for the U.S. WCPO purse seine
fleet are available are 2012–2016. Those
estimates, adjusted to an indicative fleet
size of 35 vessels, equate to annual
average catches of skipjack tuna,
yellowfin tuna, and bigeye tuna of
236,077 mt, 24,802 mt, and 4,213 mt,
respectively, or 265,091 mt in total.
Applying an indicative current Bangkok
cannery price for skipjack tuna of
$1,500 per mt to all three species, the
value of annual fleet-wide catches at
2012–2016 average levels would be
about $398 million, equivalent to a little
more than $1 million per calendar day,
on average. It should be noted that
cannery prices are fairly volatile; for
example, cannery prices are much lower
now than prices during most of 2017.
In addition to the effects described
above, the proposed limits could affect
the temporal distribution of fishing
effort in the U.S. purse seine fishery.
Since the limits would apply fleetwide—that is, they would not be
allocated to individual vessels—vessel
operators might have an incentive to
fish harder in the affected areas earlier
in each calendar year than they
otherwise would. Such a race-to-fish
effect might also be expected in the time
period between when a closure of the
fishery is announced and when it is
actually closed, which would be at least
seven calendar days. To the extent such
temporal shifts occur, they could affect
the seasonal timing of fish catches and
deliveries to canneries. The timing of
cannery deliveries by the U.S. fleet
alone (as it might be affected by a race
to fish in the EEZ or high seas) is
unlikely to have an appreciable impact
on prices, because many canneries in
the Asia-Pacific region and elsewhere
buy from the fleets of multiple nations.
A race to fish could bring costs to
affected entities if it causes vessel
operators to forego vessel maintenance
in favor of fishing or to fish in weather
or ocean conditions that they otherwise
would not. This could bring costs in
terms of the health and safety of the
crew as well as the economic
performance of the vessel.
4. Eastern High Seas Special
Management Area
This element of the proposed rule
would remove a reporting/
recordkeeping requirement, the
requirement to notify NMFS when
entering and exiting the EHSSMA. It
would also establish a prohibition on
transshipment in the EHSSMA.
Fulfillment of this element’s
requirements is not expected to require
any professional skills that the vessel
owners and operators do not already
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21759
possess. The costs of complying with
the requirements are described below to
the extent possible.
Regarding the entry/exit notices,
when NMFS established the
requirement in 2012 (final rule
published December 3, 2012; 77 FR
71501), it estimated that each report
would require about 15 minutes of labor
(at a labor cost of about $60 per hour)
and no more than $1 in communication
costs, for an estimated total cost of
compliance of about $16 per notice. At
that time, NMFS estimated that each
longline vessel would enter and exit the
EHSSMA between zero and
approximately four times per year
(requiring 0–8 notices per year at an
annual cost of $0–128), each purse seine
vessel would do so between zero and
approximately two times per year
(requiring 0–4 notices per year at an
annual cost of $0–64), and each albacore
troll vessel would do so between zero
and two times per year (requiring 0–4
notices per year at an annual cost of $0–
64). According to the notices received
by NMFS, zero longline vessels and zero
albacore troll vessels have entered the
EHSSMA from 2013 through 2017, and
there have been nine entries/exits by
purse seine fishing vessels. In any case,
under the proposed rule, commercial
fishing vessels would be relieved of
about $16 in compliance costs each time
they enter or exit the EHSSMA.
purse seine entities would be
disproportionately greater than those on
large purse seine entities.
Disproportionate Impacts
As described above, the type of the
impacts would vary greatly among
fishing gear types (i.e., longline versus
albacore troll versus purse seine), and
the magnitude of the impacts also could
vary greatly by fishing gear type (but
they are difficult to quantify and
compare). Nevertheless, all the affected
entities in the longline and albacore
troll fishing sectors are small entities, so
there would be no disproportionate
impacts between small and large entities
within those sectors. In the purse seine
fishing sector, slightly more than half
the affected entities are small entities.
The direct effect of the proposed rule
would be to constrain fishing effort by
purse seine fishing vessels, with
consequent constraining effects on both
revenues (because catches would be
less) and operating costs (because less
fishing would be undertaken). Although
some purse seine fishing entities are
larger than others, NMFS is not aware
of any differences between the small
entities and the large entities (as defined
by the RFA) in terms of their capital
costs, operating costs, or other aspects of
their businesses. Accordingly, there is
no information to suggest that the direct
adverse economic impacts on small
2. FAD Restrictions
NMFS considered in detail one
alternative to this element of the
proposed rule, but only with respect to
the timing of the two-month FAD
closure for the high seas. CMM 2017–01
allows members to choose either
November–December, as in this
proposed rule, or April–May. NMFS has
compared the expected direct economic
impacts of the two alternatives on purse
seine fishing businesses in the
regulatory impact review for the
proposed rule. The analysis finds that a
November–December closure is more
likely to have a lesser direct economic
impact on those businesses than an
April–May closure, primarily because
the later closure period is more likely to
run concurrently with a closure of the
high seas in the Convention Area to
purse seine fishing (if the fishing effort
limit in this proposed rule is reached),
in which case the FAD closure would
bring no additional economic impacts.
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Frm 00014
Fmt 4702
Sfmt 4702
Duplicating, Overlapping, and
Conflicting Federal Regulations
NMFS has not identified any Federal
regulations that duplicate, overlap with,
or conflict with the proposed
regulations.
Alternatives to the Proposed Rule
NMFS has sought to identify
alternatives that would minimize the
proposed rule’s economic impacts on
small entities (‘‘significant
alternatives’’). Taking no action could
result in lesser adverse economic
impacts than the proposed action for
affected entities (but as described below,
for some affected longline entities, the
proposed rule could be more
economically beneficial than no-action),
but NMFS does not prefer the no-action
alternative, because it would be
inconsistent with the United States’
obligations under the Convention.
Alternatives identified for each of the
four elements of the proposed rule are
discussed below.
1. Longline Bigeye Tuna Catch Limits
NMFS has not identified any
significant alternatives for this element
of the proposed rule, other than the noaction alternative.
3. Purse Seine Fishing Effort Limits
In the past, NMFS implemented the
U.S. purse seine fishing effort limits on
the high seas and in the U.S. EEZ
adopted by the Commission as a single
combined limit in the ELAPS. For this
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proposed rule, in light of CMM 2017–
01’s provision allowing the United
States to transfer some of its EEZ fishing
days to the high seas, there is a need to
separately account for the U.S. high seas
limit and the U.S. EEZ limit. Thus,
combining the two limits into a single
limit for the ELAPS is not a practical
alternative, and NMFS has not
considered it in detail.
4. Eastern High Seas Special
Management Area
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Paperwork Reduction Act
This proposed rule contains a
collection-of-information requirement
subject to review and approval by OMB
under the Paperwork Reduction Act
(PRA). This requirement has been
submitted to OMB for approval. Public
reporting burden for the daily report of
purse seine effort information is
estimated to average 10 minutes per
response, including the time for
reviewing instructions, searching
existing data sources, gathering and
maintaining the data needed, and
completing and reviewing the collection
information.
Public comment is sought regarding:
Whether this proposed collection of
information is necessary for the proper
performance of the functions of the
agency, including whether the
information shall have practical utility;
the accuracy of the burden estimate;
ways to enhance the quality, utility, and
clarity of the information to be
collected; and ways to minimize the
burden of the collection of information,
including through the use of automated
collection techniques or other forms of
information technology. Send comments
on these or any other aspects of the
collection of information to Michael D.
Tosatto, Regional Administrator, NMFS
PIRO (see ADDRESSES), and by email to
OIRA_Submission@omb.eop.gov or fax
to 202–395–5806. Notwithstanding any
other provision of the law, no person is
required to respond to, and no person
shall be subject to penalty for failure to
comply with, a collection of information
subject to the requirements of the PRA,
unless that collection of information
displays a currently valid OMB control
number.
List of Subjects in 50 CFR Part 300
Administrative practice and
procedure, Fish, Fisheries, Fishing,
Marine resources, Reporting and
recordkeeping requirements, Treaties.
14:58 May 09, 2018
For the reasons set out in the
preamble, 50 CFR part 300 is proposed
to be amended as follows:
PART 300—INTERNATIONAL
FISHERIES REGULATIONS
directed by the Pacific Islands Regional
Administrator, within 24 hours of the
end of each day that the vessel is at sea
in the Convention Area, the activity of
the vessel (e.g., setting, transiting,
searching), location and type of set, if a
set was made during that day.
*
*
*
*
*
■ 5. In § 300.222, revise paragraphs (v),
(w), (oo), and (pp) as follows:
§ 300.222
NMFS has not identified any
significant alternatives for this element
of the proposed rule, other than the noaction alternative.
VerDate Sep<11>2014
Dated: May 4, 2018.
Samuel D. Rauch, III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
Jkt 244001
Subpart O—Western and Central
Pacific Fisheries for Highly Migratory
Species
Prohibitions.
*
*
*
*
Active FAD is a FAD that is equipped
with a buoy with a clearly marked
reference number allowing its
identification and equipped with a
satellite tracking system to monitor its
position.
*
*
*
*
*
■ 3. In § 300.217, revise paragraph (b)(1)
to read as follows:
*
*
*
*
(v) Use a fishing vessel equipped with
purse seine gear to fish in an area closed
to purse seine fishing under
§ 300.223(a).
(w) Set a purse seine around, near or
in association with a FAD or a vessel,
deploy, activate, or service a FAD, or
use lights in contravention of
§ 300.223(b).
*
*
*
*
*
(oo) Transship in the Eastern High
Seas Special Management Area in
contravention of § 300.225.
(pp) Fail to submit, or ensure
submission of, a daily purse seine
fishing effort report as required in
§ 300.218(g).
*
*
*
*
*
■ 6. In § 300.223, revise paragraphs (a),
(b)(1) and (2), and add paragraph (b)(3)
to read as follows:
§ 300.217
§ 300.223
1. The authority citation for 50 CFR
part 300, subpart O, continues to read as
follows:
■
Authority: 16 U.S.C. 6901 et seq.
2. In § 300.211, add definition ‘‘Active
FAD’’ to read as follows:
■
§ 300.211
Definitions.
*
Vessel identification.
*
*
*
*
*
(b) * * *
(1) Vessels shall be marked in
accordance with the identification
requirements of § 300.336(b)(2), and if
an IRCS has not been assigned to the
vessel, then the Federal, State, or other
documentation number used in lieu of
the IRCS must be preceded by the
characters ‘‘USA’’ and a hyphen (that is,
‘‘USA-’’).
*
*
*
*
*
■ 4. In § 300.218, revise paragraphs
(a)(2)(v) and (g) to read as follows:
§ 300.218 Reporting and recordkeeping
requirements.
*
*
*
*
*
(a) * * *
(2) * * *
(v) High seas fisheries. Fishing
activities subject to the reporting
requirements of § 300.341 must be
maintained and reported in the manner
specified in § 300.341(a).
*
*
*
*
*
(g) Daily purse seine fishing effort
reports. If directed by NMFS, the owner
or operator of any fishing vessel of the
United States equipped with purse seine
gear must report to NMFS, for the
period and in the format and manner
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Fmt 4702
Sfmt 4702
*
Purse seine fishing restrictions.
*
*
*
*
*
(a) Fishing effort limits. This
paragraph establishes limits on the
number of fishing days that fishing
vessels of the United States equipped
with purse seine gear may operate in the
Convention Area in the area between
20° N latitude and 20° S latitude in a
calendar year.
(1) For the high seas there is a limit
of 1,370 fishing days per calendar year.
(2) For the U.S. EEZ there is a limit
of 458 fishing days per calendar year. If
NMFS expects that this limit will be
reached by October 1 in a given
calendar year, NMFS will publish a
notice in the Federal Register increasing
the limit for that calendar year to 558
fishing days no later than seven days
prior to October 1.
(3) NMFS will determine the number
of fishing days spent on the high seas
and in the U.S. EEZ in each calendar
year using data submitted in logbooks
and other available information. After
NMFS determines that a limit in a
calendar year is expected to be reached
by a specific future date, and at least
seven calendar days in advance of the
closure date, NMFS will publish a
notice in the Federal Register
announcing that the purse seine fishery
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in the area where the limit is expected
to be reached will be closed starting on
that specific future date and will remain
closed until the end of the calendar
year.
(4) Once a fishery closure is
announced pursuant to paragraph (a)(3)
of this section, fishing vessels of the
United States equipped with purse seine
gear may not be used to fish in the
closed area during the period specified
in the Federal Register notice, except
that such vessels are not prohibited
from bunkering during a fishery closure.
*
*
*
*
*
(b) * * *
(1) During the periods and in the areas
specified in paragraph (b)(2) of this
section, owners, operators, and crew of
fishing vessels of the United States
equipped with purse seine gear shall not
do any of the activities described below
in the Convention Area in the area
between 20° N latitude and 20° S
latitude:
(i) Set a purse seine around a FAD or
within one nautical mile of a FAD.
(ii) Set a purse seine in a manner
intended to capture fish that have
aggregated in association with a FAD or
a vessel, such as by setting the purse
seine in an area from which a FAD or
a vessel has been moved or removed
within the previous eight hours, or
setting the purse seine in an area in
which a FAD has been inspected or
handled within the previous eight
hours, or setting the purse seine in an
area into which fish were drawn by a
vessel from the vicinity of a FAD or a
vessel.
(iii) Deploy a FAD into the water.
VerDate Sep<11>2014
14:58 May 09, 2018
Jkt 244001
(iv) Repair, clean, maintain, or
otherwise service a FAD, including any
electronic equipment used in
association with a FAD, in the water or
on a vessel while at sea, except that:
(A) A FAD may be inspected and
handled as needed to identify the FAD,
identify and release incidentally
captured animals, un-foul fishing gear,
or prevent damage to property or risk to
human safety; and
(B) A FAD may be removed from the
water and if removed may be repaired,
cleaned, maintained, or otherwise
serviced, provided that it is not returned
to the water.
(v) From a purse seine vessel or any
associated skiffs, other watercraft or
equipment, do any of the following,
except in emergencies as needed to
prevent human injury or the loss of
human life, the loss of the purse seine
vessel, skiffs, watercraft or aircraft, or
environmental damage:
(A) Submerge lights under water;
(B) Suspend or hang lights over the
side of the purse seine vessel, skiff,
watercraft or equipment, or;
(C) Direct or use lights in a manner
other than as needed to illuminate the
deck of the purse seine vessel or
associated skiffs, watercraft or
equipment, to comply with navigational
requirements, and to ensure the health
and safety of the crew.
(2) The requirements of paragraph
(b)(1) of this section shall apply:
(i) From July 1 through September 30,
in each calendar year;
(ii) In any area of high seas, from
November 1 through December 31, in
each calendar year.
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Fmt 4702
Sfmt 9990
21761
(3) Activating FADs for purse seine
vessels. (i) A vessel owner, operator, or
crew of a fishing vessel of the United
States equipped with purse seine gear
shall turn on the tracking equipment of
an active FAD while the FAD is onboard
the vessel and before it is deployed in
the water.
(ii) Restrictions on Active FADs for
purse seine vessels. U.S. vessel owners
and operators of a fishing vessel of the
United States equipped with purse seine
gear shall not have more than 350
drifting active FADs per vessel in the
Convention Area at any one time.
*
*
*
*
*
■ 7. In § 300.224, revise paragraph (a)(1)
and remove paragraph (a)(2) to read as
follows:
§ 300.224
Longline fishing restrictions.
(a) * * *
(1) There is a limit of 3,554 metric
tons of bigeye tuna per calendar year
that may be captured in the Convention
Area by longline gear and retained on
board by fishing vessels of the United
States.
*
*
*
*
*
■ 8. Revise § 300.225 to read as follows:
§ 300.225 Eastern High Seas Special
Management Area.
The owner and operator of a fishing
vessel of the United States used for
commercial fishing for HMS is
prohibited from engaging in
transshipment in the Eastern High Seas
Special Management Area.
[FR Doc. 2018–09896 Filed 5–9–18; 8:45 am]
BILLING CODE 3510–22–P
E:\FR\FM\10MYP1.SGM
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Agencies
[Federal Register Volume 83, Number 91 (Thursday, May 10, 2018)]
[Proposed Rules]
[Pages 21748-21761]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-09896]
[[Page 21748]]
=======================================================================
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 300
[Docket No. 180209155-8399-01]
RIN 0648-BH77
International Fisheries; Western and Central Pacific Fisheries
for Highly Migratory Species; Fishing Limits in Purse Seine and
Longline Fisheries, Restrictions on the Use of Fish Aggregating Devices
in Purse Seine Fisheries, and Transshipment Prohibitions
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Proposed rule; request for comments.
-----------------------------------------------------------------------
SUMMARY: NMFS seeks comments on this proposed rule issued under
authority of the Western and Central Pacific Fisheries Convention
Implementation Act (WCPFC Implementation Act). The proposed rule would
implement recent decisions of the Commission for the Conservation and
Management of Highly Migratory Fish Stocks in the Western and Central
Pacific Ocean (WCPFC or Commission). These decisions include the
following management measures: limits on fishing effort by U.S. purse
seine vessels in the U.S. exclusive economic zone and on the high seas
between the latitudes of 20[deg] N and 20[deg] S in the area of
application of the Convention on the Conservation and Management of
Highly Migratory Fish Stocks in the Western and Central Pacific Ocean
(Convention); restrictions regarding the use of fish aggregating
devices (FADs) for U.S. purse seine fishing vessels; limits on the
catches of bigeye tuna by U.S. longline vessels in the Convention area;
prohibitions on U.S. vessels used to fish for highly migratory species
from engaging in transshipment in a particular area of the high seas
(the Eastern High Seas Special Management Area or EHSSMA); and removal
of existing reporting requirements for vessels transiting the EHSSMA.
The rule also would make corrections to outdated cross references in
existing regulatory text. This action is necessary to satisfy the
obligations of the United States under the Convention, to which it is a
Contracting Party.
DATES: Comments on the proposed rule must be submitted in writing by
May 25, 2018.
ADDRESSES: You may submit comments on the proposed rule and the
regulatory impact review (RIR) prepared for the proposed rule,
identified by NOAA-NMFS-2018-0050, by either of the following methods:
Electronic submission: Submit all electronic public
comments via the Federal e-Rulemaking Portal.
1. Go to www.regulations.gov/#!docketDetail;D=NOAA-NMFS-2018-0050,
2. Click the ``Comment Now!'' icon, complete the required fields,
and
3. Enter or attach your comments.
--OR--
Mail: Submit written comments to Michael D. Tosatto,
Regional Administrator, NMFS, Pacific Islands Regional Office (PIRO),
1845 Wasp Blvd., Building 176, Honolulu, HI 96818.
Instructions: Comments sent by any other method, to any other
address or individual, or received after the end of the comment period,
might not be considered by NMFS. All comments received are a part of
the public record and will generally be posted for public viewing on
www.regulations.gov without change. All personal identifying
information (e.g., name and address), confidential business
information, or otherwise sensitive information submitted voluntarily
by the sender will be publicly accessible. NMFS will accept anonymous
comments (enter ``N/A'' in the required fields if you wish to remain
anonymous).
An initial regulatory flexibility analysis (IRFA) prepared under
authority of the Regulatory Flexibility Act is included in the
Classification section of the SUPPLEMENTARY INFORMATION section of this
document.
Copies of the RIR, the 2015 programmatic environmental assessment,
and 2012 environmental assessment prepared for National Environmental
Policy Act (NEPA) purposes are available at www.regulations.gov or may
be obtained from Michael D. Tosatto, Regional Administrator, NMFS PIRO
(see address above).
Written comments regarding the burden-hour estimates or other
aspects of the collection-of-information requirements contained in this
proposed rule may be submitted to PIRO at the address listed above and
by email to [email protected] or fax to (202) 395-5806.
FOR FURTHER INFORMATION CONTACT: Rini Ghosh, NMFS PIRO, 808-725-5033.
SUPPLEMENTARY INFORMATION:
Background on the Convention
The Convention focused on the conservation and management of
fisheries for highly migratory species (HMS). The objective of the
Convention is to ensure, through effective management, the long-term
conservation and sustainable use of HMS in the Western and Central
Pacific Ocean (WCPO). To accomplish this objective, the Convention
established the Commission, which includes Members, Cooperating Non-
members, and Participating Territories (collectively referred to here
as ``members''). The United States of America is a Member. American
Samoa, Guam, and the Commonwealth of the Northern Mariana Islands
(CNMI) are Participating Territories.
As a Contracting Party to the Convention and a Member of the
Commission, the United States implements, as appropriate, conservation
and management measures and other decisions adopted by the Commission.
The WCPFC Implementation Act (16 U.S.C. 6901 et seq.), authorizes the
Secretary of Commerce, in consultation with the Secretary of State and
the Secretary of the Department in which the United States Coast Guard
is operating (currently the Department of Homeland Security), to
promulgate such regulations as may be necessary to carry out the
obligations of the United States under the Convention, including the
decisions of the Commission. The WCPFC Implementation Act further
provides that the Secretary of Commerce shall ensure consistency, to
the extent practicable, of fishery management programs administered
under the WCPFC Implementation Act and the Magnuson-Stevens Fishery
Conservation and Management Act (MSA; 16 U.S.C. 1801 et seq.), as well
as other specific laws (see 16 U.S.C. 6905(b)). The Secretary of
Commerce has delegated the authority to promulgate regulations under
the WCPFC Implementation Act to NMFS. A map showing the boundaries of
the area of application of the Convention (Convention Area), which
comprises the majority of the WCPO, can be found on the WCPFC website
at: www.wcpfc.int/doc/convention-area-map.
Background on the Conservation and Management Measures
This proposed rule would implement specific provisions of two
recent WCPFC decisions. The first decision, Conservation and Management
Measure (CMM) 2017-01, ``Conservation and Management Measure for
Bigeye,
[[Page 21749]]
Yellowfin, and Skipjack Tuna in the Western and Central Pacific
Ocean,'' was adopted by the Commission at its fourteenth regular annual
session, in December 2017, and went into effect February 2018. The
provisions of CMM 2017-01 are described in more detail below. The
second decision, CMM 2016-02, ``Conservation and Management Measures
for Eastern High Seas Pocket Special Management Area,'' revises a
previous measure regarding the EHSSMA so that vessels are no longer
required to provide reports to the Commission when entering and exiting
the EHSSMA and also prohibits all transshipment activities in the area
starting on January 1, 2019.
CMM 2017-01 is the latest in a series of CMMs devoted to the
conservation and management of tropical tuna stocks, particularly
stocks of bigeye tuna (Thunnus obesus), yellowfin tuna (Thunnus
albacares), and skipjack tuna (Katsuwonus pelamis). The stated purpose
of CMM 2017-01 is to provide for a robust transitional management
regime that ensures the sustainability of bigeye tuna, yellowfin tuna,
and skipjack tuna in the WCPO pending the Commission's establishment of
harvest strategies.
In order to achieve that stated purpose, CMM 2017-01 includes
provisions for longline and purse seine vessels that would be
implemented in this proposed rule. For longline vessels, the CMM
includes specific bigeye tuna catch limits for several WCPFC members,
including the United States. The CMM provides for a limit of 3,554
metric tons (mt) of bigeye tuna that may be caught by U.S. longline
vessels fishing in the Convention Area for calendar year 2018, which is
the same as the U.S. limit in 2016, as specified in earlier WCPFC
decisions. As in previous WCPFC CMMs on tropical tunas, CMM 2017-01
also requires any overage of the catch limit to be deducted from the
following year's limit.
Also as in previous CMMs, no limits apply to the longline fisheries
of the U.S. Participating Territories of American Samoa, Guam, and
CNMI. In addition, CMM 2017-01 includes a new provision for U.S.
longline vessels, stating that catch and effort of U.S.-flagged vessels
operating under agreements with the U.S. Participating Territories
shall be attributed to the U.S. Participating Territories.
For purse seine vessels, CMM 2017-01 includes several restrictions
on the use of FADs and provides for specific limits on fishing effort.
The first FAD restriction is similar to the one included in
previous WCPFC decisions and requires purse seine vessels to be
prohibited from fishing on FADs on the high seas and in the exclusive
economic zones (EEZs) in the Convention Area between the latitudes of
20[deg] N and 20[deg] S from July 1 through September 30 of 2018. The
second FAD restriction requires WCPFC members to establish an
additional consecutive two-month FAD prohibition period on the high
seas in the Convention Area in 2018, in either April and May or
November and December. CMM 2017-01 also includes provisions encouraging
WCPFC members to use non-entangling design and materials as well as
biodegradable materials in the construction of FADs. Finally, CMM 2017-
01 includes a provision requiring that each purse seine vessel have no
more than 350 drifting FADs with activated instrumented buoys deployed
at sea in the Convention Area at any one time through February 10,
2021. Under the CMM, an instrumented buoy is defined as a buoy with a
clearly marked reference number allowing its identification and
equipped with a satellite tracking system to monitor its position. The
CMM states that the buoy shall be activated exclusively on board the
vessel.
Under CMM 2017-01, WCPFC members must also limit their purse seine
vessels to specific fishing effort limits. The limits on U.S. purse
seine fishing effort detailed in CMM 2017-01 are similar to limits in
previous WCPFC decisions. The limits are 558 fishing days in the U.S.
EEZ and 1,270 fishing days on the high seas in the Convention Area
between the latitudes of 20[deg] N and 20[deg] S for each of the
calendar years 2018-2020. However, CMM 2017-01 also includes a new
provision for 2018 only that allows the United States to transfer 100
fishing days from its limit in the U.S. EEZ to its limit on the high
seas, and if the U.S. EEZ limit is reached by October 1, 2018, the U.S.
EEZ limit will be increased by an additional 100 fishing days, with the
expectation that the catch taken by U.S. flagged vessels and landed in
American Samoa for the American Samoa canneries is no less than the
volume landed in 2017 plus an additional 3,500 short tonnes. This new
provision was intended to alleviate the economic hardship faced by
American Samoa and its canneries when U.S. purse seine fishing limits
are reached, resulting in fishery closures.
CMM 2017-01 also includes provisions for purse seine vessels that
were in previous WCPFC decisions and that have been implemented by NMFS
in regulations that continue in force. These provisions include
requirements for purse seine vessels to retain all catch of bigeye
tuna, yellowfin tuna, and skipjack tuna, for observer coverage on purse
seine vessels, and for vessel monitoring system requirements for purse
seine vessels during the FAD closure periods.
Proposed Action
The elements of the proposed rule are detailed below. The
administrative changes that would be made to correct outdated
references in existing regulatory text are described at the end.
As described above, some of the provisions in CMM 2017-01 apply
only to calendar year 2018, while others are applicable until February
10, 2021. Because the Commission likely will continue to implement
similar management measures regarding FADs, purse seine effort limits,
and longline bigeye tuna catch limits beyond 2018, and to avoid a lapse
in the management of the fishery, NMFS is proposing to implement all of
the elements of CMM 2017-01 in this proposed rule under the authority
of the WCPFC Implementation Act, 16 U.S.C. 6904(a), so that they will
remain effective until they are replaced or amended. Because the
Commission developed CMM 2017-01 as generally a three-year conservation
and management measure (2018-2020), the supporting analyses for this
rule covers a three-year time period, understanding that these analyses
would need to be supplemented should the elements of the rule remain
effective for more than three years.
Longline Bigeye Tuna Catch Limits
The Commission-adopted longline bigeye tuna catch limit for the
United States for 2018 is 3,554 mt. As stated above, CMM 2017-01
reiterates the provision of earlier CMMs that states that any catch
overage in a given year shall be deducted from the catch limit for the
following year. The longline bigeye tuna catch limit for the United
States in 2017 was 3,138 mt (see Interim Rule; 82 FR 36341, published
August 4, 2017). Based on preliminary estimates, NMFS believes that the
2017 limit might have been exceeded, but the amount of the overage, if
it occurred, is not yet known. Thus, NMFS is proposing a calendar year
catch limit of 3,554 mt that would remain effective until replaced.
However, for 2018, it is possible that this limit would be adjusted
downward to account for any overage in 2017; the limit would similarly
be adjusted downward in future years, should any overages occur. NMFS
will determine the exact amount of the overage prior to publication of
the final rule and include the exact amount of the 2018 limit in the
final rule.
[[Page 21750]]
The calendar year longline bigeye tuna catch limit will apply only
to U.S.-flagged longline vessels operating as part of the U.S. longline
fisheries. The limit will not apply to U.S. longline vessels operating
as part of the longline fisheries of American Samoa, CNMI, or Guam.
Existing regulations at 50 CFR 300.224(b), (c), and (d) detail the
manner in which longline-caught bigeye tuna is attributed among the
fisheries of the United States and the U.S. Participating Territories.
Consistent with the basis for the limits prescribed in CMM 2017-01
and with regulations issued by NMFS to implement bigeye tuna catch
limits in U.S. longline fisheries as described below, the catch limit
is measured in terms of retained catches--that is, bigeye tuna that are
caught by longline gear and retained on board the vessel.
1. Announcement of the Limit Being Reached
As set forth under the existing regulations at 50 CFR 300.224(e),
if NMFS determines that the limit is expected to be reached in a
calendar year, NMFS will publish a notice in the Federal Register to
announce specific fishing restrictions that will be effective from the
date the limit is expected to be reached until the end of the calendar
year. NMFS will publish the notice of the restrictions at least 7
calendar days before the effective date to provide vessel owners and
operators with advance notice. Periodic forecasts of the date the limit
is expected to be reached will be made available to the public, such as
by posting on a website, to help vessel owners and operators plan for
the possibility of the limit being reached.
2. Restrictions After the Limit Is Reached
As set forth under the existing regulations at 50 CFR 300.224(f),
if the limit is reached, the restrictions that will be in effect will
include the following:
a. Retain on board, transship, or land bigeye tuna: Starting on the
effective date of the restrictions and extending through December 31 of
the given calendar year, it will be prohibited to use a U.S. fishing
vessel to retain on board, transship, or land bigeye tuna captured in
the Convention Area by longline gear, except as follows:
First, any bigeye tuna already on board a fishing vessel upon the
effective date of the restrictions can be retained on board,
transshipped, and/or landed, provided that they are landed within 14
days after the restrictions become effective. A vessel that had
declared to NMFS pursuant to 50 CFR 665.803(a) that the current trip
type is shallow-setting is not subject to this 14-day landing
restriction, so these vessels will be able to land bigeye tuna more
than 14 days after the restrictions become effective.
Second, bigeye tuna captured by longline gear can be retained on
board, transshipped, and/or landed if they are caught by a fishing
vessel registered for use under a valid American Samoa Longline Limited
Access Permit, or if they are landed in American Samoa, Guam, or CNMI.
However, the bigeye tuna must not be caught in the portion of the U.S.
EEZ surrounding the Hawaiian Archipelago, and must be landed by a U.S.
fishing vessel operated in compliance with a valid permit issued under
50 CFR 660.707 or 665.801.
Third, bigeye tuna captured by longline gear can be retained on
board, transshipped, and/or landed if they are caught by a vessel that
is included in a specified fishing agreement under 50 CFR 665.819(d),
in accordance with 50 CFR 300.224(f)(iv).
b. Transshipment of bigeye tuna to certain vessels: Starting on the
effective date of the restrictions and extending through December 31 of
the calendar year, it will be prohibited to transship bigeye tuna
caught in the Convention Area by longline gear to any vessel other than
a U.S. fishing vessel operated in compliance with a valid permit issued
under 50 CFR 660.707 or 665.801.
c. Fishing inside and outside the Convention Area: To help ensure
compliance with the restrictions related to bigeye tuna caught by
longline gear in the Convention Area, two additional, related
prohibitions would be in effect starting on the effective date of the
restrictions and extending through December 31 of the calendar year.
First, vessels are prohibited from fishing with longline gear both
inside and outside the Convention Area during the same fishing trip,
with the exception of a fishing trip that is in progress at the time
the announced restrictions go into effect. In that exceptional case,
the vessel still must land any bigeye tuna taken in the Convention Area
within 14 days of the effective date of the restrictions, as described
above. Second, if a vessel is used to fish using longline gear outside
the Convention Area and enters the Convention Area at any time during
the same fishing trip, the longline gear on the fishing vessel must be
stowed in a manner so as not to be readily available for fishing while
the vessel is in the Convention Area, specifically, the hooks, branch
or dropper lines, and floats used to buoy the mainline must be stowed
and not available for immediate use, and any power-operated mainline
hauler on deck must be covered in such a manner that it is not readily
available for use. These two prohibitions do not apply to the following
vessels: (1) Vessels on declared shallow-setting trips pursuant to 50
CFR 665.803(a); and (2) vessels operating for the purposes of this rule
as part of the longline fisheries of American Samoa, Guam, or the CNMI.
This second group includes vessels registered for use under valid
American Samoa Longline Limited Access Permits and vessels landing
their bigeye tuna catch in one of the three U.S. Participating
Territories, so long as these vessels conduct fishing activities in
accordance with the conditions described above, and vessels included in
a specified fishing agreement under 50 CFR 665.819(d), in accordance
with 50 CFR 300.224(f)(iv).
FAD Restrictions
In accordance with CMM 2017-01, NMFS proposes to establish a FAD
prohibition period from July through September in each calendar year in
the Convention Area between the latitudes of 20[deg] N and 20[deg] S
(inclusive of the EEZs and high seas in the Convention Area). Regarding
the additional consecutive two-month FAD prohibition period on the high
seas in the Convention Area, after considering the objectives of CMM
2017-01, the expected economic impacts on U.S. fishing operations and
the nation as a whole, and expected environmental and other effects,
NMFS expects that a high seas FAD prohibition period in November and
December may be somewhat more cost-effective than a FAD prohibition
period in April and May. For this reason, NMFS is proposing to
implement the high seas FAD prohibition period in November and December
for each calendar year. We specifically seek public comment on which
option is more appropriate. A comparison of the two options' expected
direct economic impacts on affected fishing businesses is provided in
the RIR.
As currently defined in 50 CFR 300.211, a FAD is ``any artificial
or natural floating object, whether anchored or not and whether
situated at the water surface or not, that is capable of aggregating
fish, as well as any object used for that purpose that is situated on
board a vessel or otherwise out of the water. The definition of FAD
does not include a vessel.'' Under this proposed rule, the regulatory
definition of a FAD would not change. Although the definition of a FAD
does not include a vessel, the restrictions during the FAD
[[Page 21751]]
prohibition periods would include certain activities related to fish
that have aggregated in association with a vessel, or drawn by a
vessel, as described below.
The prohibitions applicable to these proposed FAD-related measures
are in existing regulations at 50 CFR 300.223(b)(1)(i)-(v).
Specifically, during the July-September FAD prohibition periods in each
calendar year, and on the high seas in November and December, owners,
operators, and crew of fishing vessels of the United States equipped
with purse seine gear shall not do any of the following activities in
the Convention Area in the area between 20[deg] N latitude and 20[deg]
S latitude:
(1) Set a purse seine around a FAD or within one nautical mile of a
FAD;
(2) Set a purse seine in a manner intended to capture fish that
have aggregated in association with a FAD or a vessel, such as by
setting the purse seine in an area from which a FAD or a vessel has
been moved or removed within the previous eight hours, setting the
purse seine in an area in which a FAD has been inspected or handled
within the previous eight hours, or setting the purse seine in an area
into which fish were drawn by a vessel from the vicinity of a FAD or a
vessel;
(3) Deploy a FAD into the water;
(4) Repair, clean, maintain, or otherwise service a FAD, including
any electronic equipment used in association with a FAD, in the water
or on a vessel while at sea, except that a FAD may be inspected and
handled as needed to identify the FAD, identify and release
incidentally captured animals, un-foul fishing gear, or prevent damage
to property or risk to human safety; and a FAD may be removed from the
water and if removed may be cleaned, provided that it is not returned
to the water.
(5) From a purse seine vessel or any associated skiffs, other
watercraft or equipment, submerge lights under water; suspend or hang
lights over the side of the purse seine vessel, skiff, watercraft or
equipment, or direct or use lights in a manner other than as needed to
illuminate the deck of the purse seine vessel or associated skiffs,
watercraft or equipment, to comply with navigational requirements, and
to ensure the health and safety of the crew. These prohibitions would
not apply during emergencies as needed to prevent human injury or the
loss of human life, the loss of the purse seine vessel, skiffs,
watercraft or aircraft, or environmental damage.
This proposed rule would revise the introductory paragraph of 50
CFR 300.223(b)(1) to make it more clear that the prohibitions apply
only to owners, operators, and crew of purse seine fishing vessels.
NMFS has recently received inquiries as to whether the prohibitions
apply to the owners, operators, and crew of vessels using other gear
types. This proposed rule would also make a technical change to 50 CFR
300.223(b)(1)(iv)(B) to clarify that, during the FAD prohibition
periods, a FAD may be removed from the water to be repaired, cleaned,
maintained, or otherwise serviced, provided that it is not returned to
the water. This minor change ensures consistency with the introductory
language in that paragraph.
NMFS has recently issued final regulations to implement provisions
of a resolution adopted by the Inter-American Tropical Tuna Commission
(IATTC) that includes restrictions on the number of FADs with activated
instrumented buoys for each purse seine vessel deployed at sea in the
IATTC area at any one time (see Final Rule; 83 FR 15503, published
April 11, 2018). In order to provide some consistency to the regulated
community, NMFS is proposing similar regulations in this rule to
implement the limit regarding FADs with activated instrumented buoys
specified in CMM 2017-01.
Under the proposed rule, an active FAD is defined as a FAD that is
equipped with a buoy with a clearly marked reference number allowing
its identification and equipped with a satellite tracking system to
monitor its position, as specified by the definition of instrumented
buoy in CMM 2017-01.
CMM 2017-01 specifies that the buoy shall be activated exclusively
on board the vessel. In order to implement this provision, the proposed
rule specifies that the tracking equipment must be turned on while the
FAD is onboard the vessel and before it is deployed in the water. In
accordance with CMM 2017-01, under the proposed rule, each U.S. purse
seine vessel would have a limit of 350 active drifting FADs in the
Convention Area at any one time.
Purse Seine Fishing Effort Limits
In the past, NMFS has implemented the U.S. purse seine fishing
effort limits on the high seas and in the U.S. EEZ adopted by the
Commission as a single combined limit in a combined area of the high
seas and U.S. EEZ termed the Effort Limit Area for Purse Seine or
ELAPS. NMFS' reasoning for combining the high seas and U.S. EEZ limits
was that it afforded more operational flexibility to the fleet and
there are no substantial differences in terms of effects to living
marine resources for treating the two areas separately or combined so
long as the overall effort remained equal or less than the sum of the
two limits. For this proposed rule, in light of CMM 2017-01's provision
allowing the United States to transfer some of its EEZ days to the high
seas, there is a need to separately account for the U.S. high seas
limit and the U.S. EEZ limit. Thus, NMFS will no longer combine the two
limits under a single limit. As stated above, CMM 2017-01 specifies a
limit of 1,270 fishing days per year for the high seas and a limit of
558 fishing days per year for the U.S. EEZ. The proposed rule would
establish a limit of 1,370 fishing days on the high seas and a separate
limit of 458 fishing days in the U.S. EEZ. These numbers utilize the
provision of CMM 2017-01 provided to alleviate the economic hardship
experienced by American Samoa during a fishery closure and transfer 100
fishing days from the U.S. EEZ effort limit to the high seas effort
limit.
CMM 2017-01 also specifies that the United States may add an
additional 100 fishing days to its annual purse seine fishing effort
limit in the U.S. EEZ if the limit in the U.S. EEZ is reached by
October 1, 2018. As discussed above, NMFS is proposing to to implement
the elements of the rule so they are effective until they are amended
or replaced. Thus, under the proposed rule, when NMFS expects that the
U.S. EEZ effort limit would be reached by October 1, NMFS would publish
a notice in the Federal Register, no later than seven days prior to
October 1, to increase the U.S. EEZ effort limit by 100 fishing days
for that calendar year.
The meaning of ``fishing day'' is defined at 50 CFR 300.211; that
is, any day in which a fishing vessel of the United States equipped
with purse seine gear searches for fish, deploys a FAD, services a FAD,
or sets a purse seine, with the exception of setting a purse seine
solely for the purpose of testing or cleaning the gear and resulting in
no catch.
NMFS will monitor the number of fishing days spent in the U.S. EEZ
and on the high seas using data submitted in logbooks and other
available information. If and when NMFS determines that a limit is
expected to be reached by a specific future date, it will publish a
notice in the Federal Register announcing that the purse seine fishery
in the area where the limit is expected to be reached will be closed
starting on a specific future date and will remain closed until the end
of the calendar year. NMFS will publish that notice at least seven days
in advance of the closure date. Starting on the announced closure date,
and for the remainder of
[[Page 21752]]
calendar year, it will be prohibited for U.S. purse seine vessels to
fish in the area where the limit is expected to be reached, except that
such vessels would not be prohibited from bunkering (refueling) during
a fishery closure. NMFS published an interim rule on August 25, 2015
(see 80 FR 51478) to remove the restriction that prohibited U.S. purse
seine vessels from conducting bunkering during fishery closures of the
ELAPS. NMFS is proposing to continue those regulations as part of this
proposed rule so that bunkering would be allowed during any fishery
closures of the U.S. EEZ or high seas due to reaching a limit in a
given calendar year.
Under existing regulations at 50 CFR 300.218(g), NMFS can direct
U.S. purse seine vessel owners and operators to provide daily FAD
reports, specifying the number of purse seine sets made on FADs during
that day. NMFS promulgated this regulation to help track a limit on the
number of FAD sets that was applicable in previous years but recognizes
that this information is also valuable to help predict when a fishing
effort limit is expected to be reached with greater certainty. Thus,
under this proposed rule, NMFS would revise the existing regulations so
that NMFS can direct U.S. purse seine vessel owners and operators to
provide reports on the fishing activity of the vessel (e.g., setting,
transiting, searching), location, and type of set, in order to obtain
better data for tracking the fishing effort limits.
Eastern High Seas Special Management Area
This proposed rule would remove the requirements at 50 CFR
300.222(oo) and 50 CFR 300.225 for U.S. commercial fishing vessels to
provide reports prior to entering or exiting the EHSSMA. This proposed
rule would also prohibit all U.S. commercial fishing vessels fishing
for HMS from engaging in transshipments in the EHSSMA, beginning on
January 1, 2019.
Administrative Changes to Existing Regulations
The regulations at 50 CFR 300.217(b) and 300.218(a)(2)(v) contain
outdated cross references that would be corrected by this proposed
rule. In Sec. 300.217, paragraph (b)(1) would be revised to provide a
cross reference to Sec. 300.336(b)(2), not Sec. 300.14(b), and in
Sec. 300.218(a)(2)(v), the cross reference would be to Sec.
300.341(a) instead of to Sec. 300.17(a) and (b). Sections 300.14(b)
and 300.17(a) and (b) no longer exist and have been replaced through a
new regulatory action implementing provisions of the High Seas Fishing
Compliance Act (16 U.S.C. 5501 et seq.).
Classification
The Administrator, Pacific Islands Region, NMFS, has determined
that this proposed rule is consistent with the WCPFC Implementation Act
and other applicable laws, subject to further consideration after
public comment. Section 304(b) of the MSA provides for a 15 day comment
period for these types of fishery rules. Additionally, NMFS finds
``good cause'' under the Administrative Procedure Act that a longer
notice and comment period would be contrary to the public interest. 5
U.S.C. 553(b)(B). As described above, the first FAD prohibition period
would begin on July 1, 2018. Providing for more than 15 days advance
notice and public comment on the proposed rule increases the risk that
the Commission's FAD prohibition period will become effective prior to
the effective date of the final rule, possibly resulting in the United
States' non-compliance with its international obligations. Thus, in
order to provide the public with the opportunity to comment on this
proposed rule while ensuring that the agency has sufficient time to
consider any public comments and publish a final rule that is effective
by July 1, 2018, NMFS is providing the public with a 15-day comment
period on this proposed rule.
Coastal Zone Management Act (CZMA)
NMFS determined that this action is consistent to the maximum
extent practicable with the enforceable policies of the approved
coastal management program of American Samoa, the Commonwealth of the
Northern Mariana Islands (CNMI), Guam, and the State of Hawaii.
Determinations to Hawaii and each of the Territories were submitted on
March 12, 2018, for review by the responsible state and territorial
agencies under section 307 of the CZMA.
Executive Order 12866
This proposed rule has been determined to be not significant for
purposes of Executive Order 12866. This proposed rule is not expected
to be an Executive Order 13771 regulatory action because this proposed
rule is not significant under Executive Order 12866.
Regulatory Flexibility Act (RFA)
An initial regulatory flexibility analysis (IRFA) was prepared, as
required by section 603 of the RFA. The IRFA describes the economic
impact this proposed rule, if adopted, would have on small entities. A
description of the action, why it is being considered as well as its
objectives, and the legal basis for this action are contained in the
SUMMARY section of the preamble and in other sections of this
SUPPLEMENTARY INFORMATION section of the preamble. The analysis
follows:
Estimated Number of Small Entities Affected
For Regulatory Flexibility Act purposes only, NMFS has established
a small business size standard for businesses, including their
affiliates, whose primary industry is commercial fishing (see 50 CFR
200.2). A business primarily engaged in commercial fishing (NAICS code
114111) is classified as a small business if it is independently owned
and operated, is not dominant in its field of operation (including its
affiliates), and has combined annual receipts not in excess of $11
million for all its affiliated operations worldwide.
The proposed rule would apply to owners and operators of U.S.
commercial fishing vessels used to fish for HMS in the Convention Area,
including longline vessels (except those operating as part of the
longline fisheries of American Samoa, CNMI, or Guam), purse seine
vessels, and albacore troll vessels. Based on the number of U.S.
vessels with WCPFC Area Endorsements, which are required to fish on the
high seas in the Convention Area, the estimated numbers of affected
longline, purse seine, and albacore troll fishing vessels is 163, 37,
and 20, respectively.
Based on limited financial information about the affected fishing
fleets, and using individual vessels as proxies for individual
businesses, NMFS believes that all of the affected longline and
albacore troll vessels, and slightly more than half of the vessels in
the purse seine fleet, are small entities as defined by the RFA; that
is, they are independently owned and operated and not dominant in their
fields of operation, and have annual receipts of no more than $11.0
million. Within the purse seine fleet, analysis of average revenue, by
vessel, for the three years of 2014-2016 reveals that average annual
revenue among vessels in the fleet was about $10.2 million, and the
three-year annual averages were less than the $11 million threshold for
22 vessels in the fleet.
Recordkeeping, Reporting, and Other Compliance Requirements
The reporting, recordkeeping and other compliance requirements of
this proposed rule are described earlier in the preamble. The classes
of small entities subject to the requirements and
[[Page 21753]]
the types of professional skills necessary to fulfill the requirements
are described below for each of the first four elements of the proposed
rule. The fifth element, administrative changes to existing
regulations, is not considered further in this IRFA because it would be
of a housekeeping nature and not have any substantive effects on any
entities.
1. Longline Bigeye Tuna Catch Limits
This element of the proposed rule would not establish any new
reporting or recordkeeping requirements. The new compliance requirement
would be for affected vessel owners and operators to cease retaining,
landing, and transshipping bigeye tuna caught with longline gear in the
Convention Area if and when the bigeye tuna catch limit of 3,554 mt
(reduced by the amount of any overages in the preceding year) is
reached in any of the years 2018-2020, for the remainder of the
calendar year, subject to the exceptions and provisos described in
other sections of this SUPPLEMENTARY INFORMATION section of the
preamble. Although the restrictions that would come into effect in the
event the catch limit is reached would not prohibit longline fishing,
per se, they are sometimes referred to in this analysis as constituting
a fishery closure.
Fulfillment of this requirement is not expected to require any
professional skills that the vessel owners and operators do not already
possess. The costs of complying with this requirement are described
below to the extent possible.
Complying with this element of the proposed rule could cause
foregone fishing opportunities and result in associated economic losses
in the event that the bigeye tuna catch limit is reached in any of the
years 2018-2020 and the restrictions on retaining, landing, and
transshipping bigeye tuna are imposed for portions of those years.
These costs cannot be projected quantitatively with any certainty. The
proposed annual limit of 3,554 mt can be compared to catches in 2005-
2008, before limits were in place. The average annual catch in that
period was 4,709 mt. Based on that history, as well as fishing patterns
in 2009-2016, when limits were in place, there appears to be a
relatively high likelihood of the proposed limits being reached in
2018-2020. In 2015, for example, which saw exceptionally high catches
of bigeye tuna, the limit of 3,502 mt was estimated to have been
reached by, and the fishery was closed on, August 5 (see temporary rule
published July 28, 2015; 80 FR 44883). The fishery was subsequently re-
opened for vessels included in agreements with the governments of the
CNMI and Guam under regulations implementing Amendment 7 to the Fishery
Ecosystem Plan for Pelagic Fisheries of the Western Pacific Region
(Pelagics FEP) (50 CFR 665.819). In 2016, the limit of 3,554 mt was
estimated to have been reached by September 9, 2016, and in 2017, the
limit of 3,138 mt was estimated to have been reached by September 1,
2017. Thus, if bigeye tuna catch patterns in 2018-2020 are like those
in 2005-2008, the limit would be reached in the fourth quarter of the
year, and if they are like those in 2015, 2016, or 2017, the limit
would be reached in the third quarter of the year.
If the bigeye tuna limit is reached before the end of any of the
years 2018-2020 and the Convention Area longline bigeye tuna fishery is
consequently closed for the remainder of the calendar year, it can be
expected that affected vessels would shift to the next most profitable
fishing opportunity (which might be not fishing at all). Revenues from
that next best alternative activity reflect the opportunity costs
associated with longline fishing for bigeye tuna in the Convention
Area. The economic cost of the proposed rule would not be the direct
losses in revenues that would result from not being able to fish for
bigeye tuna in the Convention Area, but rather the difference in
benefits derived from that activity and those derived from the next
best activity. The economic cost of the proposed rule on affected
entities is examined here by first estimating the direct losses in
revenues that would result from not being able to fish for bigeye tuna
in the Convention Area as a result of the catch limit being reached.
Those losses represent the upper bound of the economic cost of the
proposed rule on affected entities. Potential next-best alternative
activities that affected entities could undertake are then identified
in order to provide a (mostly qualitative) description of the degree to
which actual costs would be lower than that upper bound.
Upper bounds on potential economic costs can be estimated by
examining the projected value of longline landings from the Convention
Area that would not be made as a result of reaching the limit. For this
purpose, it is assumed that, absent this proposed rule, bigeye tuna
catches in the Convention Area in each of the years 2018-2020 would be
5,000 mt, slightly more than the average in 2005-2008. Under this
scenario, imposition of annual limits of 3,554 mt would result in 29
percent less bigeye tuna being caught each year than under no action.
In the deep-set fishery, catches of marketable species other than
bigeye tuna would likely be affected in a similar way if vessels do not
shift to alternative activities. Assuming for the moment that ex-vessel
prices would not be affected by a fishery closure, under the proposed
rule, revenues in 2018-2020 to entities that participate exclusively in
the deep-set fishery would be approximately 29 percent less than under
no action. Average annual ex-vessel revenues (from all species) per mt
of bigeye tuna caught during 2005-2008 were about $14,190/mt (in 2014
dollars, derived from the latest available annual report on the pelagic
fisheries of the western Pacific Region (Western Pacific Regional
Fishery Management Council, 2014, Pelagic Fisheries of the Western
Pacific Region: 2012 Annual Report. Honolulu, Western Pacific Fishery
Management Council)). If there are 128 active vessels in the fleet, as
there were during 2005-2008, on average, then under the no-action
scenario of fleet-wide anual catches of 5,000 mt, each vessel would
catch 39 mt/yr, on average. Reductions of 29 percent in 2018-2020 as a
result of the proposed limits would be about 11 mt per year. Applying
the average ex-vessel revenues (from all species) of $14,190 per mt of
bigeye tuna caught, the reductions in ex-vessel revenue per vessel
would be $160,000 per year, on average.
In the shallow-set fishery, affected entities would bear limited
costs in the event of the limit being reached (but most affected
entities also participate in the deep-set fishery and might bear costs
in that fishery, as described below). The cost would be about equal to
the revenues lost from not being able to retain or land bigeye tuna
captured while shallow-setting in the Convention Area, or the cost of
shifting to shallow-setting in the eastern Pacific Ocean (EPO), which
is to the east of 150 degrees W longitude, whichever is less. In the
fourth calendar quarters of 2005-2008, almost all shallow-setting
effort took place in the EPO, and 97 percent of bigeye tuna catches
were made there, so the cost of a bigeye tuna fishery closure to
shallow-setting vessels would appear to be very limited. During 2005-
2008, the shallow-set fishery caught an average of 54 mt of bigeye tuna
per year from the Convention Area. If the proposed bigeye tuna catch
limit is reached even as early as July 31 in any of the years 2018-
2020, the Convention Area shallow-set fishery would have caught at that
point, based on 2005-2008 data, on average, 99 percent of its average
annual bigeye tuna catches. Imposition of the landings restriction at
[[Page 21754]]
that point in any of the years 2018-2020 would result in the loss of
revenues from approximately 0.5 mt (1 percent of 54 mt) of bigeye tuna,
which, based on recent ex-vessel prices, would be worth no more than
$5,000. Thus, expecting about 27 vessels to engage in the shallow-set
fishery (the annual average in 2005-2012), the average of those
potentially lost annual revenues would be no more than $200 per vessel.
The remainder of this analysis focuses on the potential costs of
compliance in the deep-set fishery.
It should be noted that the impacts on affected entities' profits
would be less than impacts on revenues when considering the costs of
operating vessels, because costs would be lower if a vessel ceases
fishing after the catch limit is reached. Variable costs can be
expected to be affected roughly in proportion to revenues, as both
variable costs and revenues would stop accruing once a vessel stops
fishing. But affected entities' costs also include fixed costs, which
are borne regardless of whether a vessel is used to fish--e.g., if it
is tied up at the dock during a fishery closure. Thus, profits would
likely be adversely impacted proportionately more than revenues.
As stated previously, actual compliance costs for a given entity
might be less than the upper bounds described above, because ceasing
fishing would not necessarily be the most profitable alternative
opportunity when the catch limit is reached. Two alternative
opportunities that are expected to be attractive to affected entities
include: (1) Deep-set longline fishing for bigeye tuna in the
Convention Area in a manner such that the vessel is considered part of
the longline fishery of American Samoa, Guam, or the CNMI; and (2)
deep-set longline fishing for bigeye tuna and other species in the EPO.
These two opportunities are discussed in detail below. Four additional
opportunities are: (3) Shallow-set longline fishing for swordfish (for
deep-setting vessels that would not otherwise do so), (4) deep-set
longline fishing in the Convention Area for species other than bigeye
tuna, (5) working in cooperation with vessels operating as part of the
longline fisheries of the Participating Territories--specifically,
receiving transshipments at sea from them and delivering the fish to
the Hawaii market, and (6) vessel repair and maintenance. A study by
NMFS of the effects of the WCPO bigeye tuna longline fishery closure in
2010 (Richmond, L., D. Kotowicz, J. Hospital and S. Allen, 2015,
Monitoring socioeconomic impacts of Hawai`i's 2010 bigeye tuna closure:
Complexities of local management in a global fishery, Ocean & Coastal
Management 106:87-96) did not identify the occurrence of any
alternative activities that vessels engaged in during the closure,
other than deep-setting for bigeye tuna in the EPO, vessel maintenance
and repairs, and granting lengthy vacations to employees. Based on
those findings, NMFS expects that alternative opportunities (3), (4),
(5) and (6) are probably unattractive relative to the first two
alternatives, and are not discussed here in any further detail. NMFS
recognizes that vessel maintenance and repairs and granting lengthy
vacations to employees are two alternative activities that might be
taken advantage of if the fishery is closed, but no further analysis of
their mitigating effects is provided here.
Before examining in detail the two potential alternative fishing
opportunities that would appear to be the most attractive to affected
entities, it is important to note that under the proposed rule, once
the limit is reached and the WCPO bigeye tuna fishery is closed,
fishing with longline gear both inside and outside the Convention Area
during the same trip would be prohibited (except in the case of a
fishing trip that is in progress when the limit is reached and the
restrictions go into effect). For example, after the restrictions go
into effect, during a given fishing trip, a vessel could be used for
longline fishing for bigeye tuna in the EPO or for longline fishing for
species other than bigeye tuna in the Convention Area, but not for
both. This reduced operational flexibility would bring costs, because
it would constrain the potential profits from alternative
opportunities. Those costs cannot be quantified.
A vessel could take advantage of the first alternative opportunity
(deep-setting for bigeye tuna in a manner such that the vessel is
considered part of the longline fishery of one of the three U.S.
Participating Territories), by three possible methods: (a) Landing the
bigeye tuna in one of the three Participating Territories, (b) holding
an American Samoa Longline Limited Access Permit, or (c) being
considered part of a Participating Territory's longline fishery, by
agreement with one or more of the three Participating Territories under
the regulations implementing Amendment 7 to the Pelagics FEP (50 CFR
665.819). In the first two circumstances, the vessel would be
considered part of the longline fishery of the Participating Territory
only if the bigeye tuna were not caught in the portion of the U.S. EEZ
around the Hawaiian Islands and were landed by a U.S. vessel operating
in compliance with a permit issued under the regulations implementing
the Pelagics FEP or the Fishery Management Plan for U.S. West Coast
Fisheries for Highly Migratory Species.
With respect to the first method of engaging in alternative
opportunity 1 (1.a.) (landing the bigeye tuna in one of the
Participating Territories), there are three potentially important
constraints. First, whether the fish are landed by the vessel that
caught the fish or by a vessel to which the fish were transshipped, the
costs of a vessel transiting from the traditional fishing grounds in
the vicinity of the Hawaiian Archipelago to one of the Participating
Territories would be substantial. Second, none of these three locales
has large local consumer markets to absorb substantial additional
landings of fresh sashimi-grade bigeye tuna. Third, transporting the
bigeye tuna from these locales to larger markets, such as markets in
Hawaii, the U.S. west coast, or Japan, would bring substantial
additional costs and risks. These cost constraints suggest that this
alternative opportunity has limited potential to mitigate the economic
impacts of the proposed rule on affected small entities.
The second method of engaging in the first alternative opportunity
(1.b.) (having an American Samoa Longline Limited Access Permit), would
be available only to the subset of the Hawaii longline fleet that has
both Hawaii and American Samoa longline permits (dual permit vessels).
Vessels that do not have both permits could obtain them if they meet
the eligibility requirements and pay the required costs. For example,
the number of dual permit vessels increased from 12 in 2009, when the
first WCPO bigeye tuna catch limit was established, to 23 in 2016. The
previously cited NMFS study of the 2010 fishery closure (Richmond et
al. 2015) found that bigeye tuna landings of dual permit vessels
increased substantially after the start of the closure on November 22,
2010, indicating that this was an attractive opportunity for dual
permit vessels, and suggesting that those entities might have
benefitted from the catch limit and the closure.
The third method of engaging in the first alternative opportunity
(1.c.) (entering into an Amendment 7 agreement), was also available in
2011-2017 (in 2011-2013, under section 113(a) of Public Law 112-55, 125
Stat. 552 et seq., the Consolidated and Further Continuing
Appropriations Act, 2012, continued by Public Law 113-6, 125 Stat. 603,
section 110, the
[[Page 21755]]
Department of Commerce Appropriations Act, 2013; hereafter, ``section
113(a)''). As a result of agreements that were in place in 2011-2014,
the WCPO bigeye tuna fishery was not closed in any of those years. In
2015, 2016, and 2017 the fishery was closed but then reopened when
agreements went into effect. Participation in an Amendment 7 agreement
would likely not come without costs to fishing businesses. As an
indication of the possible cost, the terms of the agreement between
American Samoa and the members of the Hawaii Longline Association (HLA)
in effect in 2011 and 2012 included payments totaling $250,000 from the
HLA to the Western Pacific Sustainable Fisheries Fund, equal to $2,000
per vessel. It is not known how the total cost was allocated among the
members of the HLA, so it is possible that the owners of particular
vessels paid substantially more than or less than $2,000.
The second alternative opportunity (2) (deep-set fishing for bigeye
tuna in the EPO), would be an option for affected entities only if it
is allowed under regulations implementing the decisions of the IATTC.
NMFS has issued a final rule to implement the IATTC's most recent
resolution on the management of tropical tuna stocks (83 FR 15503;
April 11, 2018). The final rule establishes an annual limit of 750 mt
on the catch of bigeye tuna in the EPO by vessels at least 24m in
length in each of the years 2018-2020. Annual longline bigeye tuna
catch limits have been in place for the EPO in most years since 2004.
Since 2009, when the limit was 500 mt, it was reached in 2013 (November
11), 2014 (October 31), and 2015 (August 12). In 2016 NMFS forecasted
that the limit would be reached July 25 and subsequently closed the
fishery, but later determined that the catch limit had not been reached
and re-opened the fishery on October 4, 2016 (81 FR 69717). The limit
was not reached in 2017.
The highly seasonal nature of bigeye tuna catches in the EPO and
the relatively high inter-annual variation in catches prevents NMFS
from making a useful prediction of whether and when the EPO limits in
2018-2020 are likely to be reached. If it is reached, this alternative
opportunity would not be available for large longline vessels, which
constitute about a quarter of the fleet.
Historical fishing patterns can provide an indication of the
likelihood of affected entities making use of the opportunity of deep-
setting in the EPO in the event of a closure in the WCPO. The
proportion of the U.S. fishery's annual bigeye tuna catches that were
captured in the EPO from 2005 through 2008 ranged from 2 percent to 22
percent, and averaged 11 percent. In 2005-2007, that proportion ranged
from 2 percent to 11 percent, and may have been constrained by the
IATTC-adoped bigeye tuna catch limits established by NMFS (no limit was
in place for 2008). Prior to 2009, most of the U.S. annual bigeye tuna
catch by longline vessels in the EPO typically was made in the second
and third quarters of the year; in 2005-2008 the percentages caught in
the first, second, third, and fourth quarters were 14, 33, 50, and 3
percent, respectively. These data demonstrate two historical patterns--
that relatively little of the bigeye tuna catch in the longline fishery
was typically taken in the EPO (11 percent in 2005-2008, on average),
and that most EPO bigeye tuna catches were made in the second and third
quarters, with relatively few catches in the fourth quarter when the
proposed catch limit would most likely be reached. These two patterns
suggest that there could be substantial costs for at least some
affected entities that shift to deep-set fishing in the EPO in the
event of a closure in the WCPO. On the other hand, fishing patterns
since 2008 suggest that a substantial shift in deep-set fishing effort
to the EPO could occur. In 2009, 2010, 2011, 2012, 2013, 2014, 2015,
and 2016 the proportions of the fishery's annual bigeye tuna catches
that were captured in the EPO were about 16, 27, 23, 19, 36, 35, 47,
and 36 percent, respectively, and most bigeye tuna catches in the EPO
were made in the latter half of the calendar years.
The NMFS study of the 2010 closure (Richmond et al. 2015) found
that some businesses--particularly those with smaller vessels--were
less inclined than others to fish in the EPO during the closure because
of the relatively long distances that would need to be travelled in the
relatively rough winter ocean conditions. The study identified a number
of factors that likely made fishing in the EPO less lucrative than
fishing in the WCPO during that part of the year, including fuel costs
and the need to limit trip length in order to maintain fish quality and
because of limited fuel storage capacity.
In addition to affecting the volume of landings of bigeye tuna and
other species, the proposed catch limits could affect fish prices,
particularly during a fishery closure. Both increases and decreases
appear possible. After a limit is reached and landings from the WCPO
are prohibited, ex-vessel prices of bigeye tuna (e.g., that are caught
in the EPO or by vessels in the longline fisheries of the three U.S.
Participating Territories), as well as of other species landed by the
fleet, could increase as a result of the constricted supply. This would
mitigate economic losses for vessels that are able to continue fishing
and landing bigeye tuna during the closure. For example, the NMFS study
of the 2010 closure (Richmond et al. 2015) found that ex-vessel prices
during the closure in December were 50 percent greater than the average
during the previous five Decembers. (It is emphasized that because it
was an observational study, neither this nor other observations of what
occurred during the closure can be affirmatively linked as effects of
the fishery closure.)
Conversely, a WCPO bigeye tuna fishery closure could cause a
decrease in ex-vessel prices of bigeye tuna and other products landed
by affected entities if the interruption in the local supply prompts
the Hawaii market to shift to alternative (e.g., imported) sources of
bigeye tuna. Such a shift could be temporary--that is, limited to 2018-
2020--or it could lead to a more permanent change in the market (e.g.,
as a result of wholesale and retail buyers wanting to mitigate the
uncertainty in the continuity of supply from the Hawaii longline
fisheries). In the latter case, if locally caught bigeye tuna fetches
lower prices because of stiffer competition with imported bigeye tuna,
then ex-vessel prices of local product could be depressed indefinitely.
The NMFS study of the 2010 closure (Richmond et al. 2015) found that a
common concern in the Hawaii fishing community prior to the closure in
November 2010 was retailers having to rely more heavily on imported
tuna, causing imports to gain a greater market share in local markets.
The study found this not to have been borne out, at least not in 2010,
when the evidence gathered in the study suggested that few buyers
adapted to the closure by increasing their reliance on imports, and no
reports or indications were found of a dramatic increase in the use of
imported bigeye tuna during the closure. The study concluded, however,
that the 2010 closure caused buyers to give increased consideration to
imports as part of their business model, and it was predicted that tuna
imports could increase during any future closure. To the extent that
ex-vessel prices would be reduced by this action, revenues earned by
affected entities would be affected accordingly, and these impacts
could occur both before and after the limit is reached, and as
described above, possibly after 2020.
The potential economic effects identified above would vary among
individual business entities, but it is not
[[Page 21756]]
possible to predict the range of variation. Furthermore, the impacts on
a particular entity would depend on both that entity's response to the
proposed rule and the behavior of other vessels in the fleet, both
before and after the catch limit is reached. For example, the greater
the number of vessels that take advantage--before the limit is
reached--of the first alternative opportunity (1), fishing as part of
one of the Participating Territory's fisheries, the lower the
likelihood that the limit would be reached.
The fleet's behavior in 2011 and 2012 is illustrative. In both
those years, most vessels in the Hawaii fleet were included in a
section 113(a) arrangement with the government of American Samoa, and
as a consequence, the U.S. longline catch limit was not reached in
either year. Thus, none of the vessels in the fleet, including those
not included in the section 113(a) arrangements, were prohibited from
fishing for bigeye tuna in the Convention Area at any time during those
two years. The fleet's experience in 2010 (before opportunities under
section 113(a) or Amendment 7 to the Pelagics FEP were available)
provides another example of how economic impacts could be distributed
among different entities. In 2010 the limit was reached and the WCPO
bigeye tuna fishery was closed on November 22. As described above, dual
permit vessels were able to continue fishing outside the U.S. EEZ
around the Hawaiian Archipelago and benefit from the relatively high
ex-vessel prices that bigeye tuna fetched during the closure.
In summary, based on potential reductions in ex-vessel revenues,
NMFS has estimated that the upper bound of potential economic impacts
of the proposed rule on affected longline fishing entities could be
roughly $160,000 per vessel per year, on average. The actual impacts to
most entities are likely to be substantially less than those upper
bounds, and for some entities the impacts could be neutral or positive
(e.g., if one or more Amendment 7 agreements are in place in 2018-2020
and the terms of the agreements are such that the U.S. longline fleet
is effectively unconstrained by the catch limits).
2. FAD Restrictions
This element of the proposed rule would not establish any new
reporting or recordkeeping requirements. The new requirement would be
for affected vessel owners and operators to comply with the FAD
restrictions described earlier in the SUPPLEMENTARY INFORMATION section
of the preamble, including FAD prohibition periods throughout the
Convention Area from July 1 through September 30 in each of the years
2018-2020 and FAD prohibition periods just on the high seas in the
Convention Area from November 1 through December 31 in each of the same
years. There would also be a limit of 350 active FADs that may be
deployed per vessel at any given time. Anecdotal information from the
U.S. purse seine fishing industry indicates that U.S. purse seine
vessels have not ever deployed more than 350 active FADs at any given
time, so NMFS does not expect that the limit would be constraining or
otherwise affect the behavior of purse seine operations, and it is not
considered further in this IRFA.
Fulfillment of the element's requirements is not expected to
require any professional skills that the vessel owners and operators do
not already possess. The costs of complying with the requirements are
described below to the extent possible.
The proposed FAD restrictions would substantially constrain the
manner in which purse seine fishing could be conducted in the specified
areas and periods in the Convention Area; in those areas and during
those periods, vessels would be able to set only on free, or
``unassociated,'' schools.
With respect to the three-month FAD closure throughout the
Convention Area: Assuming that sets would be evenly distributed through
the year, the number of annual FAD sets would be expected to be about
three-fourths the number that would occur without a seasonal FAD
closure. For example, during 2014-2016, the proportion of all sets that
were made on FADs when FAD setting was allowed was 50 percent. As an
indicative example, if the fleet makes 8,000 sets in a given year
(somewhat more than the 2014-2016 average of 7,420 sets per year) and
50 percent of those are FAD sets, it would make 4,000 FAD sets. If
there is a three-month closure and 50 percent of the sets outside the
closure are FAD sets, and sets are evenly distributed throughout each
year, the annual number of FAD sets would be 3,000. This can be
compared to the estimated 2,494 annual FAD sets that were made in 2014-
2016, on average, when there were three-month FAD closures.
With respect to the two-month high seas FAD closure: The effects of
this element are difficult to predict. If the high seas are closed to
all purse seine fishing during November-December as a result of the
fishing effort limit being reached, the high seas FAD closure during
those two months would have no additional effect whatsoever. If the
high seas are not closed to fishing, the prohibition on FAD setting
would make the high seas less favorable for fishing than they otherwise
would be, because only unassociated sets would be allowed there. It is
not possible to characterize how influential that factor would be,
however. Thus, it is not possible to predict the effects in terms of
the spatial distribution of fishing effort or the proportion of fishing
effort that is made on FADs.
With respect to both the three-month FAD closure and two-month high
seas FAD closure: As for the limits on fishing effort, vessel operators
might choose to schedule their routine maintenance periods so as to
take best advantage of the available opportunities for making FAD sets,
such as during the FAD closures. However, the limited number of vessel
maintenance facilities in the region might constrain vessel operators'
ability to do this.
It is emphasized that the indicative example given above is based
on the assumption that the FAD set ratio would be 50 percent during
periods when FAD sets are allowed, as well as that sets are distributed
evenly throughout the year. These assumptions are weak from several
perspectives, so the results should be interpreted with caution. First,
as described above, FAD set ratios have varied widely from year to
year, indicating that the conditions that dictate ``optimal'' FAD set
ratios for the fleet vary widely from year to year, and cannot be
predicted with any certainty. Second, the optimal FAD set ratio during
open periods might depend on how long and when those periods occur. For
example, FAD fishing might be particularly attractive soon after a
closed period during which FADs aggregated fish but were not fished on.
These factors are not explicitly accounted for in this analysis, but
the 50 percent FAD ratio used in this analysis was taken from 2014-
2016, when there was a three-month FAD closure, so it is probably a
better indicator for the action alternatives than FAD set ratios for
years prior to 2009, when no seasonal FAD closures were in place. With
respect to the distribution of sets through the year, the existence of
collective limits on fishing effort might create an incentive for
individual vessels to fish harder earlier in the year than they
otherwise would, resulting in a ``race to fish.'' Limitations on
fishing effort throughout the Convention Area could cause vessels to
fish (irrespective of set type or the timing of FAD closures) harder
earlier in a given year than they would without the limits. However,
any such effect is not expected to be great, because most vessels in
the fleet tend to fish virtually full time, leaving little
[[Page 21757]]
flexibility to increase fishing effort at any particular time of the
year.
Vessels in the U.S. WCPO purse seine fleet make both unassociated
sets and FAD sets when not constrained by regulation, so one type of
set is not always more valuable or efficient than the other type. Which
set type is optimal at any given time is a function of immediate
conditions in and on the water, but probably also of such factors as
fuel prices (unassociated sets involve more searching time and thus
tend to bring higher fuel costs than FAD sets) and market conditions
(e.g., FAD fishing, which tends to result in greater catches of lower-
value skipjack tuna and smaller yellowfin tuna and bigeye tuna than
unassociated sets, might be more attractive and profitable when
canneries are not rejecting small fish). Clearly, the ability to do
either type of set is valuable, and constraints on the use of either
type can be expected to bring adverse economic impacts to fishing
operations. Thus, the greater the constraints on the ability to make
FAD sets, the greater the expected economic impacts of the action.
Because the factors affecting the relative value of FAD sets and
unassociated sets are many, and the relationships among them are not
well known, it is not possible to quantify the expected economic
impacts of the FAD restrictions. However, it appears reasonable to
conclude the following: First, the FAD restrictions would adversely
impact producer surplus relative to the no-action alternative. The fact
that the fleet has made such a substantial portion of its sets on FADs
in the past indicates that prohibiting the use of FADs in the specified
areas and periods could bring substantial costs and/or revenue losses.
Second, vessel operators might be able to mitigate the impacts of the
FAD restrictions by scheduling their routine vessel and equipment
maintenance during the FAD closures, but this opportunity might be
constrained by the limited vessel maintenance facilities in the region.
3. Purse Seine Fishing Effort Limits
This element of the proposed rule would not establish any new
reporting or recordkeeping requirements, but the existing ``Daily FAD
reports'' required at 50 CFR 300.218(g) would be slightly revised, and
renamed ``Daily purse seine fishing effort reports'' and would slightly
modify the type of information collected.
There would be annual limits of 1,370 and 458 fishing days on the
high seas and in the U.S. EEZ, respectively, in the Convention Area. In
addition, there would be a mechanism to increase the U.S. EEZ limit in
a given year to 558 fishing days if 458 fishing days are used by
October 1 of that year.
Fulfillment of this element's requirements is not expected to
require any professional skills that the vessel owners and operators do
not already possess. The costs of complying with the requirements are
described below to the extent possible.
Regarding the modification to the daily reporting requirement, the
specific information required in the reports would be slightly modified
from those of the existing ``Daily FAD reports,'' but the costs of
compliance are not expected to change.
Regarding the fishing effort limits, if and when the fishery on the
high seas or in the U.S. EEZ is closed as a result of a limit being
reached in any of the years 2018-2020, owners and operators of U.S.
purse seine vessels would have to cease fishing in that area for the
remainder of the calendar year. Closure of the fishery in either of
those areas could thereby cause foregone fishing opportunities and
associated economic losses if the area contains preferred fishing
grounds during such a closure. Historical fishing rates in the two
areas give a rough indication of the likelihood of the limits being
reached.
Regarding the U.S. EEZ, from 2009 through 2017 (NMFS has only
preliminary estimates for 2017), no more than 50 percent of the
proposed limit of 458 fishing days was ever used (and no more than the
41 percent of the possible limit of 558 fishing days). This history
suggests a relatively low likelihood of the proposed EEZ limit being
reached in 2018-2020. However, the allowance for an extra 100 fishing
days if the 458 fishing days are used by October 1 could provide an
incentive for the fleet to use more fishing days in the EEZ than it
otherwise would. Furthermore, this would be the first time that
separate limits would be established for the EEZ and the high seas, so
the incentives for individual vessels in the fleet would change. A
minority of the fleet is authorized to fish in the U.S. EEZ (8 of the
33 vessels currently licensed under the South Pacific Tuna Treaty
(SPTT) \1\ have fishery endorsements on their U.S. Coast Guard
Certificates of Documentation, which are required to fish in the U.S.
EEZ, and 1 of the other 4 purse seine vessels with WCPFC Area
Endorsements has a fishery endorsement), and with a separate limit for
the U.S. EEZ, this minority might take more advantage of it than it has
in the past.
---------------------------------------------------------------------------
\1\ The majority of U.S. purse seine fishing activity in the
Convention Area takes place in the waters of Pacific Island Parties
to the SPTT (PIPs), pursuant to the terms of the SPTT.
---------------------------------------------------------------------------
Regarding the high seas from 2009 through 2017, between 31 and 135
percent of the proposed limit of 1,370 fishing days was used, and at
least 100 percent was used in three of the nine years. In two years,
2015 and 2016, the ELAPS was closed for part of the year (starting June
15 in 2015, and September 2 in 2016), so more fishing effort might have
occurred in those two years were there no limits. This history suggests
a substantial likelihood of the proposed high seas limit being reached
in any of the years 2018-2020.
Two factors could have a substantial influence on the amount of
fishing effort in the U.S. EEZ and on the high seas in 2018-2020:
First, the number of fishing days available in foreign waters (the
fleet's main fishing grounds) pursuant to the SPTT will influence the
incentive to fish outside those waters, including the U.S. EEZ and high
seas. Second, El Ni[ntilde]o--Southern Oscillation (ENSO) conditions
will influence where the best fishing grounds are.
Regarding fishing opportunities in foreign waters, in December
2016, the United States and PIPs agreed upon a revised SPTT, and under
this new agreement U.S. purse seine fishing businesses can purchase
fishing days in the EEZs of the PIPs. There are limits on the number of
such ``upfront'' fishing days that may be purchased. These limits can
influence the amount of fishing in other areas, such as the U.S. EEZ
and the high seas, as well as the EPO. For example, if the number of
available upfront fishing days is relatively small, fishing effort in
the U.S. EEZ and/or high seas might be relatively great. In fact, the
number of upfront days available for the Kiribati EEZ, which has
traditionally constituted important fishing grounds for the U.S. fleet,
is notably small--only 300 fishing days per year. However, the new SPTT
regime provides for U.S. purse seine fishing businesses to purchase
``additional'' fishing days through direct bilateral agreements with
the PIPs. NMFS cannot project how many additional days will be
purchased in any given years, so cannot gauge how the limits on upfront
days might influence fishing effort in the U.S. EEZ or on the high
seas. Limits on upfront days are therefore not considered here any
further.
Additionally, effective January 1, 2015, Kiribati prohibited
commercial fishing in the Phoenix Islands Protected Area, which is a
large portion of the Kiribati EEZ around the Phoenix Islands. These
limitations in the Kiribati
[[Page 21758]]
EEZ in 2015 probably made fishing in the ELAPS more attractive than it
otherwise would be.
Regarding El Ni[ntilde]o Southern Oscillation (ENSO) conditions,
the eastern areas of the WCPO tend to be comparatively more attractive
to the U.S. purse seine fleet during El Ni[ntilde]o events, when warm
surface water spreads from the western Pacific to the eastern Pacific
and large, valuable yellowfin tuna become more vulnerable to purse
seine fishing and trade winds lessen in intensity. Consequently, the
U.S. EEZ and high seas, much of which is situated in the eastern range
of the fleet's fishing grounds, is likely to be more important fishing
grounds to the fleet during El Ni[ntilde]o events (as compared to
neutral or La Ni[ntilde]a events). This is supported by there being a
statistically significant correlation between annual average per-vessel
fishing effort in the ELAPS and the Oceanic Ni[ntilde]o Index, a common
measure of ENSO conditions, over the life of the SPTT through 2010.
El Ni[ntilde]o conditions were present in 2015 and in the first
half of 2016, and might have contributed to the relatively high rates
of fishing in the ELAPS in those years. ENSO neutral conditions began
in the latter half of 2016, and continued until the fourth quarter of
2017, when there was a shift to La Ni[ntilde]a conditions, which
persisted through early 2018 (and which is consistent with the moderate
rates of fishing in the ELAPS in 2017). As of February 8, 2018, the
National Weather Service states that a transition from La Ni[ntilde]o
to ENSO-neutral conditions is likely (~55 percent chance) in March-May
of 2018 (NWS 2018). Thus ENSO conditions might have a negative
influence on fishing in the U.S. EEZ and the high seas early in 2018
and a largely neutral influence for the rest of 2018. Their influence
on fishing effort in 2019 and 2020 cannot be predicted with any
certainty.
Another potentially important factor is that the EEZ and high seas
limits would be competitive limits, so their establishment could cause
a ``race to fish'' in the two areas. That is, vessel operators might
seek to take advantage of the limited number of fishing days available
in the areas before the limits are reached, and fish harder in the
ELAPS than they would if there were no limits. On the one hand, any
such race-to-fish effect might be reflected in the history of fishing
in the ELAPS, described above. On the other hand, anecdotal information
from the fishing industry suggests that the limits might have been
internally allocated by the fleet, which might have tempered any race
to fish. It is not known whether the industry intends to internally
allocate the proposed limits.
In summary, although difficult to predict, either the U.S. EEZ or
high seas limits could be reached in any of the years 2018-2020,
especially the high seas limits. If either limit is reached in a given
year, the fleet would be prohibited from fishing in that area for the
remainder of the calendar year.
The closure of any fishing grounds for any amount of time can be
expected to bring adverse impacts to affected entities (e.g., because
the open area might, during the closed period, be less productive than
the closed area, and vessels might use more fuel and spend more time
having to travel to open areas). The severity of the impacts of a
closure would depend greatly on the length of the closure and where the
most favored fishing grounds are during the closure. A study by NMFS
(Chan, V. and D. Squires. 2016. Analyzing the economic impacts of the
2015 ELAPS closure. NMFS Internal Report) estimated that the overall
losses to the combined sectors of the vessels, canneries and vessel
support companies from the 2015 ELAPS closure ranged from $11 million
and $110 million depending on the counterfactual period considered.
These results suggest that there were impacts from the ELAPS closure on
the American Samoa economy and a connection between U.S. purse seine
vessels and the broader American Samoa economy.
If either the U.S. EEZ or high seas is closed, possible next-best
opportunities for U.S. purse seine vessels fishing in the WCPO include
fishing in the other of the two areas, fishing in foreign EEZs inside
the Convention Area, fishing outside the Convention Area in EPO, and
not fishing.
With respect to fishing in the U.S. EEZ or on the high seas: If the
U.S. EEZ were closed, the high seas would be available to the fleet
until its limit is reached. If the high seas were closed, the U.S. EEZ
would be available until its limit is reached, but only for the vessels
with fishery endorsements on their Certificates of Documentation
(currently 9, including 8 vessels with SPTT licenses and one additional
vessel without).
With respect to fishing in the Convention Area in foreign EEZs: As
described above, under the SPTT the fleet might have substantial
fishing days available in the Pacific Island country EEZs that dominate
the WCPO, but it is not possible to predict how many fishing days will
be available to the fleet as a whole or to individual fishing
businesses.
With respect to fishing in the EPO: The fleet has generally
increased its fishing operations in the EPO since 2014, and as of 2017,
there were 17 purse seine vessel in the WCPO fleet that are also listed
on the IATTC Vessel Register. In order to fish in the EPO, a vessel
must be on the IATTC's Regional Vessel Register and categorized as
active (50 CFR 300.22(b)), which involves fees of about $14.95 per
cubic meter of well space per year (e.g., a vessel with 1,200 m\3\ of
well space would be subject to annual fees of $17,940). (As an
exception to this rule, an SPTT-licensed vessel is allowed to make one
fishing trip in the EPO each year without being categorized as active
on the IATTC Regional Vessel Register. The trip must not exceed 90 days
in length, and there is an annual limit of 32 such trips for the entire
SPTT-licensed fleet (50 CFR 300.22(b)(1)).) The number of U.S. purse
seine vessels in the WCPO fleet that have opted to be categorized as
such has increased in the last few years from zero to 17, probably
largely a result of constraints on fishing days in the WCPO and/or
uncertainty in future access arrangements under the SPTT. This suggests
an increasing attractiveness of fishing in the EPO, in spite of the
costs associated with doing so. However, in 2018 vessels probably will
not have the opportunity to fish in the EPO year-round. To implement a
recent decision of the IATTC, NMFS has published a final rule that
requires purse seine vessels to choose between two EPO fishing
prohibition periods each year in 2018-2020: July 29-October 8 or
November 9-January 19 (72 days in either case). Thus, the opportunity
to fish in the EPO might be constrained, depending on when the U.S. EEZ
and/or high seas in the WCPFC Area is closed, and which EPO closure
period a given vessel operator chooses.
With respect to not fishing at all during a closure of the U.S. EEZ
or high seas: This would mean a loss of any revenues from fishing.
However, many of the vessels' variable operating costs would be avoided
in that case, and it is possible that for some vessels a portion of the
time might be used for productive activities like vessel and equipment
maintenance.
The opportunity costs of engaging in next-best opportunities in the
event of a closure are not known, so the potential impacts cannot be
quantified. However, to give an indication of the magnitude of possible
economic impacts to producers in the fishery (i.e., an indication of
the upper bound of those impacts), information on revenues per day is
provided here.
[[Page 21759]]
The last five years for which catch estimates for the U.S. WCPO
purse seine fleet are available are 2012-2016. Those estimates,
adjusted to an indicative fleet size of 35 vessels, equate to annual
average catches of skipjack tuna, yellowfin tuna, and bigeye tuna of
236,077 mt, 24,802 mt, and 4,213 mt, respectively, or 265,091 mt in
total. Applying an indicative current Bangkok cannery price for
skipjack tuna of $1,500 per mt to all three species, the value of
annual fleet-wide catches at 2012-2016 average levels would be about
$398 million, equivalent to a little more than $1 million per calendar
day, on average. It should be noted that cannery prices are fairly
volatile; for example, cannery prices are much lower now than prices
during most of 2017.
In addition to the effects described above, the proposed limits
could affect the temporal distribution of fishing effort in the U.S.
purse seine fishery. Since the limits would apply fleet-wide--that is,
they would not be allocated to individual vessels--vessel operators
might have an incentive to fish harder in the affected areas earlier in
each calendar year than they otherwise would. Such a race-to-fish
effect might also be expected in the time period between when a closure
of the fishery is announced and when it is actually closed, which would
be at least seven calendar days. To the extent such temporal shifts
occur, they could affect the seasonal timing of fish catches and
deliveries to canneries. The timing of cannery deliveries by the U.S.
fleet alone (as it might be affected by a race to fish in the EEZ or
high seas) is unlikely to have an appreciable impact on prices, because
many canneries in the Asia-Pacific region and elsewhere buy from the
fleets of multiple nations. A race to fish could bring costs to
affected entities if it causes vessel operators to forego vessel
maintenance in favor of fishing or to fish in weather or ocean
conditions that they otherwise would not. This could bring costs in
terms of the health and safety of the crew as well as the economic
performance of the vessel.
4. Eastern High Seas Special Management Area
This element of the proposed rule would remove a reporting/
recordkeeping requirement, the requirement to notify NMFS when entering
and exiting the EHSSMA. It would also establish a prohibition on
transshipment in the EHSSMA.
Fulfillment of this element's requirements is not expected to
require any professional skills that the vessel owners and operators do
not already possess. The costs of complying with the requirements are
described below to the extent possible.
Regarding the entry/exit notices, when NMFS established the
requirement in 2012 (final rule published December 3, 2012; 77 FR
71501), it estimated that each report would require about 15 minutes of
labor (at a labor cost of about $60 per hour) and no more than $1 in
communication costs, for an estimated total cost of compliance of about
$16 per notice. At that time, NMFS estimated that each longline vessel
would enter and exit the EHSSMA between zero and approximately four
times per year (requiring 0-8 notices per year at an annual cost of $0-
128), each purse seine vessel would do so between zero and
approximately two times per year (requiring 0-4 notices per year at an
annual cost of $0-64), and each albacore troll vessel would do so
between zero and two times per year (requiring 0-4 notices per year at
an annual cost of $0-64). According to the notices received by NMFS,
zero longline vessels and zero albacore troll vessels have entered the
EHSSMA from 2013 through 2017, and there have been nine entries/exits
by purse seine fishing vessels. In any case, under the proposed rule,
commercial fishing vessels would be relieved of about $16 in compliance
costs each time they enter or exit the EHSSMA.
Disproportionate Impacts
As described above, the type of the impacts would vary greatly
among fishing gear types (i.e., longline versus albacore troll versus
purse seine), and the magnitude of the impacts also could vary greatly
by fishing gear type (but they are difficult to quantify and compare).
Nevertheless, all the affected entities in the longline and albacore
troll fishing sectors are small entities, so there would be no
disproportionate impacts between small and large entities within those
sectors. In the purse seine fishing sector, slightly more than half the
affected entities are small entities. The direct effect of the proposed
rule would be to constrain fishing effort by purse seine fishing
vessels, with consequent constraining effects on both revenues (because
catches would be less) and operating costs (because less fishing would
be undertaken). Although some purse seine fishing entities are larger
than others, NMFS is not aware of any differences between the small
entities and the large entities (as defined by the RFA) in terms of
their capital costs, operating costs, or other aspects of their
businesses. Accordingly, there is no information to suggest that the
direct adverse economic impacts on small purse seine entities would be
disproportionately greater than those on large purse seine entities.
Duplicating, Overlapping, and Conflicting Federal Regulations
NMFS has not identified any Federal regulations that duplicate,
overlap with, or conflict with the proposed regulations.
Alternatives to the Proposed Rule
NMFS has sought to identify alternatives that would minimize the
proposed rule's economic impacts on small entities (``significant
alternatives''). Taking no action could result in lesser adverse
economic impacts than the proposed action for affected entities (but as
described below, for some affected longline entities, the proposed rule
could be more economically beneficial than no-action), but NMFS does
not prefer the no-action alternative, because it would be inconsistent
with the United States' obligations under the Convention. Alternatives
identified for each of the four elements of the proposed rule are
discussed below.
1. Longline Bigeye Tuna Catch Limits
NMFS has not identified any significant alternatives for this
element of the proposed rule, other than the no-action alternative.
2. FAD Restrictions
NMFS considered in detail one alternative to this element of the
proposed rule, but only with respect to the timing of the two-month FAD
closure for the high seas. CMM 2017-01 allows members to choose either
November-December, as in this proposed rule, or April-May. NMFS has
compared the expected direct economic impacts of the two alternatives
on purse seine fishing businesses in the regulatory impact review for
the proposed rule. The analysis finds that a November-December closure
is more likely to have a lesser direct economic impact on those
businesses than an April-May closure, primarily because the later
closure period is more likely to run concurrently with a closure of the
high seas in the Convention Area to purse seine fishing (if the fishing
effort limit in this proposed rule is reached), in which case the FAD
closure would bring no additional economic impacts.
3. Purse Seine Fishing Effort Limits
In the past, NMFS implemented the U.S. purse seine fishing effort
limits on the high seas and in the U.S. EEZ adopted by the Commission
as a single combined limit in the ELAPS. For this
[[Page 21760]]
proposed rule, in light of CMM 2017-01's provision allowing the United
States to transfer some of its EEZ fishing days to the high seas, there
is a need to separately account for the U.S. high seas limit and the
U.S. EEZ limit. Thus, combining the two limits into a single limit for
the ELAPS is not a practical alternative, and NMFS has not considered
it in detail.
4. Eastern High Seas Special Management Area
NMFS has not identified any significant alternatives for this
element of the proposed rule, other than the no-action alternative.
Paperwork Reduction Act
This proposed rule contains a collection-of-information requirement
subject to review and approval by OMB under the Paperwork Reduction Act
(PRA). This requirement has been submitted to OMB for approval. Public
reporting burden for the daily report of purse seine effort information
is estimated to average 10 minutes per response, including the time for
reviewing instructions, searching existing data sources, gathering and
maintaining the data needed, and completing and reviewing the
collection information.
Public comment is sought regarding: Whether this proposed
collection of information is necessary for the proper performance of
the functions of the agency, including whether the information shall
have practical utility; the accuracy of the burden estimate; ways to
enhance the quality, utility, and clarity of the information to be
collected; and ways to minimize the burden of the collection of
information, including through the use of automated collection
techniques or other forms of information technology. Send comments on
these or any other aspects of the collection of information to Michael
D. Tosatto, Regional Administrator, NMFS PIRO (see ADDRESSES), and by
email to [email protected] or fax to 202-395-5806.
Notwithstanding any other provision of the law, no person is required
to respond to, and no person shall be subject to penalty for failure to
comply with, a collection of information subject to the requirements of
the PRA, unless that collection of information displays a currently
valid OMB control number.
List of Subjects in 50 CFR Part 300
Administrative practice and procedure, Fish, Fisheries, Fishing,
Marine resources, Reporting and recordkeeping requirements, Treaties.
Dated: May 4, 2018.
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 300 is
proposed to be amended as follows:
PART 300--INTERNATIONAL FISHERIES REGULATIONS
Subpart O--Western and Central Pacific Fisheries for Highly
Migratory Species
0
1. The authority citation for 50 CFR part 300, subpart O, continues to
read as follows:
Authority: 16 U.S.C. 6901 et seq.
0
2. In Sec. 300.211, add definition ``Active FAD'' to read as follows:
Sec. 300.211 Definitions.
* * * * *
Active FAD is a FAD that is equipped with a buoy with a clearly
marked reference number allowing its identification and equipped with a
satellite tracking system to monitor its position.
* * * * *
0
3. In Sec. 300.217, revise paragraph (b)(1) to read as follows:
Sec. 300.217 Vessel identification.
* * * * *
(b) * * *
(1) Vessels shall be marked in accordance with the identification
requirements of Sec. 300.336(b)(2), and if an IRCS has not been
assigned to the vessel, then the Federal, State, or other documentation
number used in lieu of the IRCS must be preceded by the characters
``USA'' and a hyphen (that is, ``USA-'').
* * * * *
0
4. In Sec. 300.218, revise paragraphs (a)(2)(v) and (g) to read as
follows:
Sec. 300.218 Reporting and recordkeeping requirements.
* * * * *
(a) * * *
(2) * * *
(v) High seas fisheries. Fishing activities subject to the
reporting requirements of Sec. 300.341 must be maintained and reported
in the manner specified in Sec. 300.341(a).
* * * * *
(g) Daily purse seine fishing effort reports. If directed by NMFS,
the owner or operator of any fishing vessel of the United States
equipped with purse seine gear must report to NMFS, for the period and
in the format and manner directed by the Pacific Islands Regional
Administrator, within 24 hours of the end of each day that the vessel
is at sea in the Convention Area, the activity of the vessel (e.g.,
setting, transiting, searching), location and type of set, if a set was
made during that day.
* * * * *
0
5. In Sec. 300.222, revise paragraphs (v), (w), (oo), and (pp) as
follows:
Sec. 300.222 Prohibitions.
* * * * *
(v) Use a fishing vessel equipped with purse seine gear to fish in
an area closed to purse seine fishing under Sec. 300.223(a).
(w) Set a purse seine around, near or in association with a FAD or
a vessel, deploy, activate, or service a FAD, or use lights in
contravention of Sec. 300.223(b).
* * * * *
(oo) Transship in the Eastern High Seas Special Management Area in
contravention of Sec. 300.225.
(pp) Fail to submit, or ensure submission of, a daily purse seine
fishing effort report as required in Sec. 300.218(g).
* * * * *
0
6. In Sec. 300.223, revise paragraphs (a), (b)(1) and (2), and add
paragraph (b)(3) to read as follows:
Sec. 300.223 Purse seine fishing restrictions.
* * * * *
(a) Fishing effort limits. This paragraph establishes limits on the
number of fishing days that fishing vessels of the United States
equipped with purse seine gear may operate in the Convention Area in
the area between 20[deg] N latitude and 20[deg] S latitude in a
calendar year.
(1) For the high seas there is a limit of 1,370 fishing days per
calendar year.
(2) For the U.S. EEZ there is a limit of 458 fishing days per
calendar year. If NMFS expects that this limit will be reached by
October 1 in a given calendar year, NMFS will publish a notice in the
Federal Register increasing the limit for that calendar year to 558
fishing days no later than seven days prior to October 1.
(3) NMFS will determine the number of fishing days spent on the
high seas and in the U.S. EEZ in each calendar year using data
submitted in logbooks and other available information. After NMFS
determines that a limit in a calendar year is expected to be reached by
a specific future date, and at least seven calendar days in advance of
the closure date, NMFS will publish a notice in the Federal Register
announcing that the purse seine fishery
[[Page 21761]]
in the area where the limit is expected to be reached will be closed
starting on that specific future date and will remain closed until the
end of the calendar year.
(4) Once a fishery closure is announced pursuant to paragraph
(a)(3) of this section, fishing vessels of the United States equipped
with purse seine gear may not be used to fish in the closed area during
the period specified in the Federal Register notice, except that such
vessels are not prohibited from bunkering during a fishery closure.
* * * * *
(b) * * *
(1) During the periods and in the areas specified in paragraph
(b)(2) of this section, owners, operators, and crew of fishing vessels
of the United States equipped with purse seine gear shall not do any of
the activities described below in the Convention Area in the area
between 20[deg] N latitude and 20[deg] S latitude:
(i) Set a purse seine around a FAD or within one nautical mile of a
FAD.
(ii) Set a purse seine in a manner intended to capture fish that
have aggregated in association with a FAD or a vessel, such as by
setting the purse seine in an area from which a FAD or a vessel has
been moved or removed within the previous eight hours, or setting the
purse seine in an area in which a FAD has been inspected or handled
within the previous eight hours, or setting the purse seine in an area
into which fish were drawn by a vessel from the vicinity of a FAD or a
vessel.
(iii) Deploy a FAD into the water.
(iv) Repair, clean, maintain, or otherwise service a FAD, including
any electronic equipment used in association with a FAD, in the water
or on a vessel while at sea, except that:
(A) A FAD may be inspected and handled as needed to identify the
FAD, identify and release incidentally captured animals, un-foul
fishing gear, or prevent damage to property or risk to human safety;
and
(B) A FAD may be removed from the water and if removed may be
repaired, cleaned, maintained, or otherwise serviced, provided that it
is not returned to the water.
(v) From a purse seine vessel or any associated skiffs, other
watercraft or equipment, do any of the following, except in emergencies
as needed to prevent human injury or the loss of human life, the loss
of the purse seine vessel, skiffs, watercraft or aircraft, or
environmental damage:
(A) Submerge lights under water;
(B) Suspend or hang lights over the side of the purse seine vessel,
skiff, watercraft or equipment, or;
(C) Direct or use lights in a manner other than as needed to
illuminate the deck of the purse seine vessel or associated skiffs,
watercraft or equipment, to comply with navigational requirements, and
to ensure the health and safety of the crew.
(2) The requirements of paragraph (b)(1) of this section shall
apply:
(i) From July 1 through September 30, in each calendar year;
(ii) In any area of high seas, from November 1 through December 31,
in each calendar year.
(3) Activating FADs for purse seine vessels. (i) A vessel owner,
operator, or crew of a fishing vessel of the United States equipped
with purse seine gear shall turn on the tracking equipment of an active
FAD while the FAD is onboard the vessel and before it is deployed in
the water.
(ii) Restrictions on Active FADs for purse seine vessels. U.S.
vessel owners and operators of a fishing vessel of the United States
equipped with purse seine gear shall not have more than 350 drifting
active FADs per vessel in the Convention Area at any one time.
* * * * *
0
7. In Sec. 300.224, revise paragraph (a)(1) and remove paragraph
(a)(2) to read as follows:
Sec. 300.224 Longline fishing restrictions.
(a) * * *
(1) There is a limit of 3,554 metric tons of bigeye tuna per
calendar year that may be captured in the Convention Area by longline
gear and retained on board by fishing vessels of the United States.
* * * * *
0
8. Revise Sec. 300.225 to read as follows:
Sec. 300.225 Eastern High Seas Special Management Area.
The owner and operator of a fishing vessel of the United States
used for commercial fishing for HMS is prohibited from engaging in
transshipment in the Eastern High Seas Special Management Area.
[FR Doc. 2018-09896 Filed 5-9-18; 8:45 am]
BILLING CODE 3510-22-P