Fisheries Off West Coast States; Pacific Coast Groundfish Fishery; Seabird Avoidance Measures, 71975-71981 [2015-29249]
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Federal Register / Vol. 80, No. 222 / Wednesday, November 18, 2015 / Rules and Regulations
vessel accounting for bluefin tuna
bycatch using quota allocation available
to the vessel (either through its own
quota share or leasing allocation from
another vessel). Bluefin tuna must be
accounted for as described at
§ 635.15(b)(4) and (5).
Based on Atlantic bluefin tuna dealer
data and IBQ system data, as of
November 10, 2015, 33,484 lb (15.2 mt)
of bluefin tuna has been landed, and 90
lb (<0.1 mt) of bluefin tuna has been
discarded dead in the NED; an
additional 36 bluefin tuna have been
reported as retained through Vessel
Monitoring System (VMS) bluefin tuna
catch reports. These 36 retained bluefin
tuna reported via VMS equate to
approximately 17,460 lb (7.9 mt) of
additional catch, which brings the total
estimated bluefin tuna catch from the
NED to 51,034 lb (23.2 mt). Based on
this data, NMFS has determined that the
25 mt set-aside will be filled on
November 12, 2015.
Because the NED the quota has been
reached, vessels are notified that they
must account for any bycatch of bluefin
tuna (landings and/or dead discards) in
the NED using IBQ allocation as
specified in the regulations at
§ 635.15(b)(8). Vessel owners will have
to account retroactively for their bluefin
tuna bycatch with IBQ to the date that
the separate quota was reached. NMFS
currently anticipates that date will be
November 12, 2015, but will notify
relevant vessel owners of the precise
date when we have complete NED catch
data.
With respect to quota accounting for
the fishery as whole, bluefin bycatch
(landings and dead discards) from the
NED beyond the 25 mt set-aside will
count toward the Longline category
annual baseline subquota. For 2015,
NMFS delayed certain regulatory
requirements requiring vessels with
pelagic longline gear to have a
minimum amount of IBQ quota before
departing on fishing trips, thus allowing
such vessels to fish with pelagic
longline gear even if they have quota
debt. However, we specified that quota
debt will accrue throughout the 2015
fishing year, and vessels will be
responsible for accounting for all of
their bluefin bycatch at the end of the
year. If, by the end of 2015, a permit
holder does not have adequate IBQ
allocation to settle their vessel’s quota
debt, the vessel’s allocation will be
reduced in the amount equal to the
quota debt in the subsequent year or
years until the quota debt is fully
accounted for. Vessels with a negative
balance will have to satisfy the quota
debt before departing on any trips in
2016.
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NMFS will continue to monitor
bluefin tuna bycatch by vessels fishing
with pelagic longline gear using VMS
and dealer data, as well as monitor the
accounting for such catch in the IBQ
system, to ensure that vessels are
accountable for their bluefin bycatch
and that quotas are managed consistent
with the 2006 Consolidated HMS FMP
and our international quota obligations.
For fishery updates, fishermen may call
the Atlantic Tunas Information Line at
(888) 872–8862 or (978) 281–9260,
access the following internet address:
www.hmspermits.gov.
71975
Information relevant to this
final rule, which includes a final
environmental assessment (EA), are
available from William W. Stelle, Jr.,
Regional Administrator, West Coast
Region, NMFS, 7600 Sand Point Way
NE., Seattle, WA 98115–0070.
Electronic copies of this final rule are
also available at the NMFS West Coast
Region Web site: https://
www.westcoast.fisheries.noaa.gov.
ADDRESSES:
FOR FURTHER INFORMATION CONTACT:
Sarah Williams, 206–526–4646; (fax)
206–526–6736; sarah.williams@
noaa.gov.
Authority: 16 U.S.C. 971 et seq. and 1801
et seq.
SUPPLEMENTARY INFORMATION:
Dated: November 12, 2015.
Emily H. Menashes,
Acting Director, Office of Sustainable
Fisheries, National Marine Fisheries Service.
Background
[FR Doc. 2015–29400 Filed 11–13–15; 4:15 pm]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 660
[Docket No. 140214140–5999–01]
RIN 0648–BD92
Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery;
Seabird Avoidance Measures
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
This final rule implements a
Seabird Avoidance Program in the
Pacific Coast Groundfish Fishery. The
rule was recommended by the Pacific
Fishery Management Council (Council)
in November 2013 to minimize the take
of ESA-listed short-tailed albatross
(Phoebastria albatrus). A 2012 U.S. Fish
and Wildlife Service (USFWS)
Biological Opinion (Opinion) required
NMFS to initiate implementation of
regulations within 2 years that mandate
the use of seabird avoidance measures
by vessels greater than or equal to 55
feet length overall (LOA) using bottom
longline gear to harvest groundfish. The
seabird avoidance measures, including
streamer lines that deter birds from
ingesting baited hooks, are modeled
after a similar regulatory program in
effect for the Alaskan groundfish
fishery.
SUMMARY:
DATES:
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The purpose of this rule is to reduce
interactions between ESA-listed
seabirds and groundfish longline gear.
This final rule amends the regulations
governing the Pacific Coast Groundfish
Fishery (fishery) to require seabird
avoidance measures—specifically, the
use of streamer lines and related
provisions similar to those currently
mandated in the Alaskan groundfish
fishery—by vessels 55 ft LOA or greater
in the bottom longline fishery.
This rule is needed to minimize takes
of endangered short-tailed albatross and
comply with a 2012 Biological Opinion
(Opinion) issued by the U.S. Fish and
Wildlife Service.
In sum, the rule:
• Requires the use of streamer lines in
the commercial longline fishery of the
Pacific Coast Groundfish Fishery for
non-tribal vessels 55 feet in length or
greater;
• Requires vessels to deploy one or
two streamer lines depending on the
type of longline gear being set;
• Requires that streamer lines meet
technical specifications and be available
for inspection; and
• Allows for a rough weather
exemption from using streamer lines for
safety purposes. The threshold for the
rough weather exemption is a Gale
Warning as issued by the National
Weather Service.
The rule is designed to be consistent
with the requirements of the Opinion
and responsive to issues raised through
the public process and consultation
with experts.
Comments and Responses
NMFS solicited public comment on
the proposed seabird avoidance
measures (79 FR 53401, September 9,
2014). The comment period ended
October 9, 2014. NMFS received seven
comment letters from individuals or
organizations. The letters are available
in their entirety from NMFS (see
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ADDRESSES) or at the following web
address: https://www.regulations.gov/#
!docketBrowser;rpp=25;po=0;dct=PS;D=
NOAA-NMFS-2014-0099. For clarity in
responding, comments have been
organized into the following categories,
which are addressed in turn below:
Monitoring, Gear Specification and
Performance, Scope, Environmental
Assessment, and Other.
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Monitoring
Comment 1: Observers or Electronic
Monitoring should be used to monitor
compliance with performance and
materials standards in order for the
seabird avoidance regulations to be
effective.
Response: NMFS agrees. The West
Coast Groundfish Observer Program
(WCGOP) developed and implemented a
sampling protocol in 2009 and 2010 to
characterize the longline fleet and its
use of seabird avoidance gear. The
protocol was designed to provide data
on the types of streamer lines being
deployed and the performance of the
streamers insofar as it can be
determined visually. For example,
observers recorded the number of
streamer lines deployed; where the
streamer lines were deployed relative to
sinking hooks; the deployment of towed
objects on the end of streamer lines; the
extent of streamer lines relative to the
water surface; the number of streamers
on each line; the color and material of
the streamers; the distance between
streamers; the distance from the stern to
the first streamer; and a range of
measurements associated with the
design and performance of streamer
lines. The information can be used by
managers to assess the performance of
streamer lines at sea. Observers
currently record the type of seabird
avoidance gear being used. In 2015, this
will include a distinction between
single and double streamer lines.
Observers also record the catch of
seabirds which is the ultimate
determinant of the performance of
seabird avoidance measures. In response
to this comment and the ongoing need
to characterize the use of seabird
avoidance gear, WCGOP will refine the
sampling protocol for implementation
in 2016 or earlier as opportunity allows.
Comment 2: NMFS should use either
human observers or electronic means to
monitor seabird interactions in the atsea hake fishery because there is a high
overlap of fishing areas with albatross
occurrence; and, the fleet’s practice of
continuous offal discharge may attract
birds. It is known that bird strikes with
trawl cables cause high mortality of
albatross in other regions.
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Response: As described in the BiOp,
seabirds are attracted to offal plumes
and can strike trawl cables, sonar cables,
or become entangled on nets at or near
the surface. Such interactions are
unlikely to be detected as they do not
show up on the deck to be sampled
under normal observer protocols. NMFS
agrees with the need to characterize
seabird mortality in the at-sea hake
fishery and is committed to developing
a monitoring plan; however, there are
significant issues associated with both
the observer program and electronic
monitoring that make it premature to
choose a specific course of action at this
time.
Regarding the observer program,
observer duties are carefully prescribed
according to priorities developed to
support fishery management decisions.
The main priority is to monitor catch
composition—including seabirds that
come up with the trawl. Each processing
vessel carries two observers. Observers
subsample the catch to collect data used
to estimate catch composition. In
addition, the observers collect biological
data from groundfish, protected species
including seabirds, and prohibited
species. Observers are required to be in
the factory, below deck, for the majority
of their sampling. Observation of trawl
and sonar cables would occur on deck
and take a significant amount of time
away from catch composition sampling.
Electronic monitoring is in a
developmental stage for West Coast
groundfish fisheries and significant
research is necessary before it is
practicable to apply to seabird
monitoring in the at-sea hake fishery.
Similar to observers, electronic
monitoring is being developed to
monitor catch composition. There have
not been formal investigations into the
effectiveness and practicability of
training cameras away from the deck to
monitor trawl and sonar cables.
NMFS will pursue a monitoring plan
by working through the Council and its
appropriate committees, such as the
Council’s ESA Working Group that was
established specifically to implement
the Opinion; and, ad hoc committees
composed to advise the Council on the
development of electronic monitoring.
Such committees offer a formal
opportunity to engage the Council in
monitoring and conservation issues and
is the most appropriate opportunity to
develop an effective and practicable
monitoring plan.
Comment 3: Observers should record
wind speed to associate weather data
with seabird interactions in order to
assess impacts associated with the
rough weather exemption.
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Response: NMFS agrees. Observers
currently record weather conditions
using the Beaufort scale for any sighting
or take of an ESA-listed species,
including short-tailed albatross.
Weather observations are currently
made at the time the observer
encounters the animal which, in
longline fisheries, is usually during the
retrieval of gear. The weather conditions
during retrieval may be different from
when the mortality event occurred,
which is typically as gear is being set.
For this reason, and in response to this
comment, NMFS will modify WCGOP
sampling protocols so that observers
record weather conditions as longlines
are being set for at least a subset of
hauls. The modified protocol may not
be fully effective until 2016 due to
program logistics.
Comment 4: NMFS should monitor
the free streamer line program to
determine if lines are being used
properly, ensure plastic components of
the streamer lines are not illegally
discarded at sea, and to avoid wasteful
spending of U.S. tax dollars that are
funding the program.
Response: NMFS agrees. Consistent
with the response to Comment 1 above,
observers are monitoring the
performance of streamer lines at sea.
Observers also monitor for violations of
the International Convention for the
Prevention of Pollution from Ships
(MARPOL) that prohibits the at-sea
disposal of all plastics. Observers
document compliance infractions and
suspected violations in their logbook
and complete a written statement during
debriefing.
Gear Specification and Performance
Comment 5: NMFS should exempt the
requirement to use streamer lines during
longline sets that take place at night.
Based on 20 years of personal
experience, I have never encountered a
seabird on a night set. Requiring
streamer lines during night sets imposes
a safety risk and inconvenience without
reducing seabird mortality.
Response: To address this comment,
NMFS conducted an analysis to
determine if seabird catch rates differ
when the longline gear is set in the dark
versus the light. The analysis shows a
reduction in the seabird bycatch when
the gear is set at night and could
provide an option for fishermen to not
use streamer lines at night in the future.
At this time, NMFS has determined that
providing a night-setting exemption is
outside the scope of the proposed rule.
NMFS received comments from the
Council on including an exemption for
night setting, including comments from
the U.S. Coast Guard representative,
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which supported the exemption but
requested further investigation into an
exemption rather than inclusion in the
regulations at this time.
Comment 6: The proposed rule is
inadequate and ineffective as a seabird
bycatch mitigation measure. Best
practices, as adopted by the Agreement
on the Conservation of Albatrosses and
Petrels (ACAP), do not support only
using streamer lines to deter seabirds.
Streamer lines should be used in
conjunction with other measures such
as weighting the line to maximize sink
rates; actively deterring birds from
baited hooks by using bird scaring lines;
and, setting at night.
Response: NMFS disagrees that the
proposed rule is inadequate; however,
NMFS agrees that the full range of best
practices described by ACAP is an
important component of effective
seabird conservation. NMFS and the
Council considered alternatives that
would have implemented the full suite
of ACAP best practices in the EA (see
ADDRESSES). The measures described in
the comment (other than streamer lines)
are being pursued by non-regulatory
means. NMFS and partner organizations
are working with fishermen to
encourage voluntary implementation of
measures consistent with ACAP best
practices, including sinking hooks
quickly, night setting, and managing
discharge of offal and bait. Fishermen
on the West Coast have a significant
incentive to avoid seabirds in order to
ensure baited hooks are available to
catch fish. A hook with a seabird on it
precludes that opportunity and impacts
the profitability of fishing operations.
For this reason and as analyzed in the
EA, NMFS and the Council determined
that a non-regulatory approach to the
full suite of best practices was the most
appropriate at this time. This does not
preclude regulatory approaches in the
future should monitoring indicate that
voluntary efforts are not sufficient. To
that end, NMFS has worked to establish
the ESA Working Group to consider
new information and formulate advice
on adaptive management to the Council.
Comment 7: The proposed streamer
line specifications are inadequate and
ineffective. The specifications used
under the Convention on the
Conservation of Antarctic Marine Living
Resources (CCAMLR) should be
adopted, including: (1) Minimum of
height at stern of 7 m; (2) minimum
streamer line length of 150 m and the
use of a drogue; (3) no rough weather
exemption; and, (4) the aerial extent of
streamer lines should be stipulated as a
performance standard (100 m is
suggested).
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Response: NMFS disagrees that the
proposed streamer line specifications
are inadequate and ineffective. The
CCAMLR regulations reflect the
development of seabird avoidance
measures designed for the specific
fisheries and seabird assemblages. The
sub-Antarctic fisheries governed under
CCAMLR include primarily Patagonia
toothfish (Dissostichus eleginoides),
which is fished with the Spanish
method of bottom longlining, where the
gear is more buoyant than that used on
the West Coast. The majority of the
vessels are large (30–50 m) and deploy
gear from the stern at speeds of 10–13
knots. The prevalent seabirds
incidentally taken are albatrosses and
petrels species, many of which dive to
foraging depths that are substantially
deeper than the North Pacific albatross
and other species that occur off the West
Coast.
In contrast, West Coast groundfish
fisheries target primarily sablefish,
which is a demersal species fished with
bottom gear consisting of groundlines to
which relatively short gangions are
attached. In general, vessels deploy gear
from the stern. The prevalent seabird
species incidentally taken are fulmars,
gulls, and albatrosses.
The CCAMLR streamer line
specifications are designed to provide
more aerial coverage than is necessary
or appropriate for West Coast
groundfish fisheries. The minimum
stern height, line length, and aerial
extent specifications cover a greater area
because longlines used in those fisheries
are more buoyant and extend further
behind the vessel than occurs in
fisheries covered under this rule, and
because the seabird species taken in
CCAMLR fisheries dive to deeper
depths than those on the West Coast.
The specifications in this rule were
recommended based on extensive
research that demonstrated them to be
effective in Alaskan groundfish
fisheries, where the targeted fish
species, vessels, and seabirds are similar
and, in some cases, identical. More
information on this research and the
effectiveness of the streamer line
specification in this final rule is
available in the Opinion or EA (see
ADDRESSES).
NMFS notes however that preliminary
research by Washington Sea Grant
indicates that some vessels in West
Coast groundfish fisheries are using
floats on gangions to avoid predation by
non-marketable bottom fish (i.e.,
hagfish). The floats may reduce the
effectiveness of these streamer line
specifications by keeping baited hooks
in the water column past the extent of
streamer lines. It is unclear at this time
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how widespread the use of floats is,
how much it influences seabird catch
rates, and what alternatives are
appropriate if floats are determined to
be a significant issue affecting seabird
catch rates. Because the research is
preliminary, and because the streamer
line specifications in this final rule have
been demonstrated to be effective in
reducing seabird mortality and are
required by the Opinion, NMFS is
finalizing this rule and will continue to
monitor its effectiveness to determine if
future changes are warranted. NMFS is
also continuing to support Washington
Sea Grant in conducting this research
and has worked to establish the ESA
Working Group to consider new
information and formulate advice on
adaptive management to the Council.
Comment 8: Vessels should not be
permitted to take excessive numbers of
seabirds. Vessels should be required to
move to night setting for the remainder
of the fishing season if seabird bycatch
exceeds 0.01 seabirds per 1000 hooks in
a set, or until the vessel is able to
demonstrate a line sink rate of a
minimum of 0.3 m/second to 15 m
depth. Applying a performance standard
quickly halts lax and ineffective fishing
practices.
Response: A system does not
currently exist within NMFS to hold
individual vessels accountable for
seabird mortality in real time. Similarly,
it is not feasible for NMFS to monitor
and enforce sink rates of longline gear
on individual vessels. More
importantly, NMFS does not believe
such a system is necessary given that
the final regulations are designed to
effectively reduce seabird bycatch in the
fleet where most of the seabirds are
taken.
Scope of the Regulations
Comment 9: Vessels smaller than 55
ft should be required to use seabird
avoidance measures to minimize the
chance that such vessels will take ESAlisted short-tailed albatross and other
seabirds.
Response: NMFS agrees that there
may be a risk to short-tailed albatross
from longline vessels under 55 ft;
however, it would be premature to
require that they use seabird avoidance
gear at this time. The Opinion specifies
that this rule apply to larger vessels for
the following reasons: (1) Vessels under
55 ft have not been observed to interact
with short-tailed albatross; (2) vessels
under 55 ft are being encouraged
through formal outreach described in
the EA (see ADDRESSES) to deploy
seabird avoidance measures on a
voluntary basis; and, (3) NMFS does not
have an appropriate technical
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specification for streamer lines proven
to be safe for smaller vessels. To address
the latter, Washington Sea Grant is
conducting research to determine safe
and effective seabird avoidance
measures for vessels under 55 ft. In
limiting the requirement specified in the
Opinion to vessels 55 ft and over,
USFWS further required NMFS to adapt
management as appropriate in response
to that research and ongoing monitoring.
NMFS is committed to review new
information as it becomes available to
determine if these regulations should be
adapted to cover smaller vessels. To that
end, NMFS has worked to establish the
ESA Working Group to consider new
information and formulate advice on
adaptive management to the Council.
Comment 10: NMFS should require
that seabird avoidance measures be
deployed in the at-sea hake fishery
because there is a high overlap of
fishing areas with albatross occurrence
and the fleet’s practice of continuous
offal discharge that may attract birds. It
is known that bird strikes with trawl
cables cause high mortality of albatross
in other regions.
Response: NMFS agrees that there is
a potential threat to seabirds associated
with the at-sea hake fishery; however, it
is premature to regulate that fishery at
this time. As described in the response
to Comment 2 above, NMFS will pursue
a monitoring plan to assess the level of
threat and appropriate responses.
Regulating the at-sea hake fishery is
outside the scope of this rule, which is
focused on implementing requirements
stipulated by USFWS in the Opinion.
USFWS recognized the potential for
interaction between seabirds and the atsea hake fishery but determined that the
focus of seabird avoidance measures
should be the longline fleet. In doing so,
USFWS further required NMFS to adapt
management as appropriate in response
to new information. NMFS is committed
to reviewing new information as it
becomes available to determine if these
regulations should be adapted to other
fisheries such as the at-sea hake fishery.
To that end, NMFS has worked to
establish the ESA Working Group to
consider new information and formulate
advice on adaptive management to the
Council.
Environmental Assessment
Comment 11: The EA must analyze
whether short-tailed albatross are at
higher risk of entanglement during high
wind events.
Response: NMFS agrees. The EA, in
Section 4.1.1, acknowledges the
uncertainty regarding seabird behavior
during rough weather and concludes the
exemption is not expected to
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significantly influence the overall
reduction in seabird bycatch. NMFS is
not aware of additional information
pertinent to assessing the effects of
rough weather on seabird encounters by
longline vessels but will continue to
monitor observer data and adapt
management as new information
becomes available. To that end, NMFS
has worked to establish the ESA
Working Group to consider new
information and formulate advice on
adaptive management to the Council.
Comment 12: The EA does not
adequately assess the effects of vessels
under 55 ft on short-tailed albatross.
Response: NMFS disagrees.
Consistent with the response to
Comment 9, the EA acknowledges there
may be a risk to short-tailed albatross
from vessels under 55 ft and
incorporates voluntary conservation and
ongoing research into analysis of the
status quo alternative (See ADDRESSES).
Other
Comment 13: The groundfish fishery
operates in important seabird foraging
habitat as well as critical habitat of
leatherback sea turtles and green
sturgeon. Streamer lines may have
unintended consequences if they are
lost overboard. Streamers should be
made of plant-based materials in order
to minimize the biological risks
associated with ingestion by marine
animals.
Response: In response to this
comment, NMFS consulted with
NOAA’s Marine Debris Program to
determine if there is evidence for
streamer lines as marine debris in areas
such as Alaska and Hawaii, where there
are existing requirements for longline
vessels to use them. Streamers (the
plastic component of streamer lines)
have been observed during shoreline
clean-ups in Alaska; however, the
quantity relative to other marine debris
is very low. Reports from shoreline
cleanups in Hawaii have not noted the
presence of streamers. Given the low
incidence of observed streamers, it
would not be reasonable to change
design specifications at this time.
Streamer lines are constructed of
materials, including plastics, sufficient
to withstand at-sea conditions. A change
in the material specifications would
require significant research to ensure
streamer lines would continue to
function by reducing seabird
entanglement. Such research is not
practicable at this time. NMFS notes
that intentional disposal at sea is
unlikely because fishermen are subject
to MARPOL, which prohibits the at-sea
disposal of plastics.
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Comment 14: NMFS should ensure
authorization of fisheries complies with
the Migratory Bird Treaty Act (MBTA).
Response: NMFS agrees. The final
regulations are consistent with the
MBTA.
Comment 15: NMFS should provide,
and crewmembers should be required to
attend, workshops to identify and
distinguish short-tailed albatross from
other albatrosses and also to safely
release live short-tailed albatrosses.
Response: NMFS agrees that
education and outreach is an important
component of seabird conservation;
however, NMFS disagrees that it should
be required. NMFS has provided
funding for Washington Sea Grant to
conduct outreach that has included
mailings to all fixed-gear permit
holders, port meetings with fishermen,
an internet site, and educational
exhibits at trade shows. The material
includes information on seabird
avoidance, species identification, and
how to handle hooked albatross. NMFS
believes that these efforts have been
successful in educating fishermen on
issues related to seabird bycatch.
Comment 16: A number of
commenters were in support of the
proposed regulations.
Response: NMFS acknowledges this
comment.
Changes from the Proposed Rule
There are no substantial changes from
the proposed rule. NMFS made one
modification to re-locate the regulatory
text so that it is grouped with other
groundfish regulations. The goal of this
change is to locate the seabird
avoidance program regulations near
other programs that apply to multiple
sectors of the groundfish fishery.
Classification
Pursuant to section 304(b)(1)(A) of the
MSA, the NMFS Assistant
Administrator has determined that this
final rule is consistent with the Pacific
Coast Groundfish FMP, other provisions
of the MSA, and other applicable law.
NMFS and the Council prepared a
final Environmental Assessment (EA)
for this regulation and concluded that
there would not be a significant impact
on the human environment as a result
of this rule. A copy of the EA is
available from NMFS (see ADDRESSES).
This final rule has been determined to
be not significant for purposes of
Executive Order 12866.
The Regulatory Flexibility Act
requires Federal agencies to conduct a
full RFAA unless the agency can certify
that the proposed and/or final rule
would not have a significant economic
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Federal Register / Vol. 80, No. 222 / Wednesday, November 18, 2015 / Rules and Regulations
impact on a substantial number of small
entities.
The Chief Counsel for Regulation of
the Department of Commerce certified
to the Chief Counsel for Advocacy of the
Small Business Administration during
the proposed rule stage that this action
would not have a significant economic
impact on a substantial number of small
entities. The factual basis for the
certification was published in the
proposed rule and is not repeated here.
No comments were received regarding
this certification. As a result, a
regulatory flexibility analysis was not
required and none was prepared.
Section 212 of the Small Business
Regulatory Enforcement Fairness Act of
1996 states that, for each rule or group
of related rules for which an agency is
required to prepare a FRFA, the agency
shall publish one or more guides to
assist small entities in complying with
the rule, and shall designate such
publications as ‘‘small entity
compliance guides.’’ The agency shall
explain the actions a small entity is
required to take to comply with a rule
or group of rules. As part of this
rulemaking process, a public notice that
also serves as small entity compliance
guide (the guide) was prepared. Copies
of this final rule are available from the
West Coast Regional Office, and the
guide will be posted on the NMFS West
Coast Region Web site and emailed to
the groundfish fishery listserve. The
guide and this final rule will be
available upon request.
NMFS issued Biological Opinions
under the Endangered Species Act
(ESA) on August 10, 1990, November
26, 1991, August 28, 1992, September
27, 1993, May 14, 1996, and December
15, 1999, pertaining to the effects of the
Groundfish FMP fisheries on Chinook
salmon (Puget Sound, Snake River
spring/summer, Snake River fall, upper
Columbia River spring, lower Columbia
River, upper Willamette River,
Sacramento River winter, Central Valley
spring, California coastal), coho salmon
(Central California coastal, southern
Oregon/northern California coastal),
chum salmon (Hood Canal summer,
Columbia River), sockeye salmon (Snake
River, Ozette Lake), and steelhead
(upper, middle and lower Columbia
River, Snake River Basin, upper
Willamette River, central California
coast, California Central Valley, south/
central California, northern California,
southern California). These biological
opinions have concluded that
implementation of the FMP is not
expected to jeopardize the continued
existence of any endangered or
threatened species under the
jurisdiction of NMFS, or result in the
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14:36 Nov 17, 2015
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destruction or adverse modification of
critical habitat.
NMFS issued a Supplemental
Biological Opinion on March 11, 2006,
concluding that neither the higher
observed bycatch of Chinook in the
2005 whiting fishery nor new data
regarding salmon bycatch in the
groundfish bottom trawl fishery
required a reconsideration of its prior
‘‘no jeopardy’’ conclusion. NMFS also
reaffirmed its prior determination that
implementation of the FMP is not likely
to jeopardize the continued existence of
any of the affected ESUs. Lower
Columbia River coho (70 FR 37160, June
28, 2005) and Oregon Coastal coho (73
FR 7816, February 11, 2008) were
relisted as threatened under the ESA.
The 1999 biological opinion concluded
that the bycatch of salmonids in the
Pacific whiting fishery were almost
entirely Chinook salmon, with little or
no bycatch of coho, chum, sockeye, and
steelhead.
On December 7, 2012, NMFS
completed a biological opinion
concluding that the groundfish fishery
is not likely to jeopardize non-salmonid
marine species including listed
eulachon, green sturgeon, humpback
whales, Steller sea lions, and
leatherback sea turtles. The opinion also
concluded that the fishery is not likely
to adversely modify critical habitat for
green sturgeon and leatherback sea
turtles. An analysis included in the
same document as the opinion
concluded that the fishery is not likely
to adversely affect green sea turtles,
olive ridley sea turtles, loggerhead sea
turtles, sei whales, North Pacific right
whales, blue whales, fin whales, sperm
whales, Southern Resident killer
whales, Guadalupe fur seals, or the
critical habitat for Steller sea lions.
West Coast pot fisheries for sablefish
are considered Category II fisheries
under the Marine Mammal Protection
Act (MMPA), indicating occasional
interactions. All other West Coast
groundfish fisheries, including the trawl
fishery, are considered Category III
fisheries under the MMPA, indicating a
remote likelihood of or no known
serious injuries or mortalities to marine
mammals. MMPA section 101(a)(5)(E)
requires that NMFS authorize the taking
of ESA-listed marine mammals
incidental to U.S. commercial fisheries
if it makes the requisite findings,
including a finding that the incidental
mortality and serious injury from
commercial fisheries will have a
negligible impact on the affected species
or stock. As noted above, NMFS
concluded in its biological opinion for
the 2012 groundfish fisheries that these
fisheries were not likely to jeopardize
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71979
Steller sea lions or humpback whales.
The eastern distinct population segment
of Steller sea lions was delisted under
the ESA on November 4, 2013 (78 FR
66140). On September 4, 2013, based on
its negligible impact determination
dated August 28, 2013, NMFS issued a
permit for a period of 3 years to
authorize the incidental taking of
humpback whales by the sablefish pot
fishery (78 FR 54553).
NMFS has reinitiated section 7
consultation on the Pacific Coast
Groundfish FMP with respect to its
effects on listed salmonids. In the event
the consultation identifies either
reasonable and prudent alternatives to
address jeopardy concerns, or
reasonable and prudent measures to
minimize incidental take, NMFS would
coordinate with the Council to put
additional alternatives or measures into
place, as required. After reviewing the
available information, NMFS has
concluded that, consistent with sections
7(a)(2) and 7(d) of the ESA, this action
will not jeopardize any listed species,
would not adversely modify any
designated critical habitat, and will not
result in any irreversible or irretrievable
commitment of resources that would
have the effect of foreclosing the
formulation or implementation of any
reasonable and prudent alternative
measures.
On November 21, 2012, the U.S. Fish
and Wildlife Service (FWS) issued a
biological opinion concluding that the
groundfish fishery will not jeopardize
the continued existence of the shorttailed albatross. The 2012 Opinion
evaluated the risks of continued
operation of the Pacific Coast
groundfish fishery on ESA-listed
seabirds, including short-tailed
albatross. The 2012 Opinion included a
Term and Condition requiring NMFS to
promulgate regulations mandating the
use of streamer lines by longline vessels
55 feet LOA or greater, patterned on the
Alaska streamer line regulations.
Accordingly, for the fishery to be
exempt from the ESA section 9
prohibition regarding take of a listed
species, NMFS must initiate
implementation of streamer line
regulations by November 21, 2014. The
2012 Opinion anticipates the yearly
average take of one short-tailed albatross
killed from longline hooks or trawl
cables. As the short-tailed albatross
population is expanding, it is expected
to result in more interactions with the
Pacific Coast Groundfish Fisheries. This
action would implement one of the
Terms and Conditions of the 2012
Opinion and reduce the risk of
exceeding the take limits of short-tailed
albatross, which in turn would reduce
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Federal Register / Vol. 80, No. 222 / Wednesday, November 18, 2015 / Rules and Regulations
the risk of economic harm to the fishing
industry that could result from the
incidental take limit being exceeded.
The FWS also concurred that the fishery
is not likely to adversely affect the
marbled murrelet, California least tern,
southern sea otter, bull trout, or bull
trout critical habitat.
This final rule does not contain a
collection-of-information requirement
subject to review and approval by OMB
under the Paperwork Reduction Act
(PRA).
This final rule was developed after
meaningful collaboration, through the
Council process, with the tribal
representative on the Council. The
regulations have no direct effect on the
tribes and were deemed by the Council
as ‘‘necessary or appropriate’’ to
implement the FMP as amended.
List of Subjects in 50 CFR Part 660
Administrative practice and
procedure, American Samoa, Fisheries,
Fishing, Guam, Hawaiian natives,
Indians, Northern Mariana Islands,
Reporting and recordkeeping
requirements.
Dated: November 10, 2015.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
For the reasons stated in the
preamble, 50 CFR part 660 is amended
as follows:
PART 660—FISHERIES OFF WEST
COAST STATES
1. The authority citation for part 660
continues to read as follows:
■
Authority: 16 U.S.C. 1801 et seq., 16
U.S.C. 773 et seq., and 16 U.S.C. 7001 et seq.
2. In § 660.11, add paragraph (6)(i)(A)
and reserved paragraph (6)(i)(B) to the
definition of ‘‘Fishing gear’’ and add the
definition for ‘‘Seabird’’ in alphabetical
order to read as follows:
■
§ 660.11
General definitions.
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*
*
*
*
*
Fishing gear * * *
(6) * * *
(i) * * *
(A) Snap gear means a type of bottom
longline gear where the hook and
gangion are attached to the groundline
using a mechanical fastener or snap.
(B) [Reserved]
*
*
*
*
*
Seabird means those bird species that
habitually obtain their food from the sea
below the low water mark.
*
*
*
*
*
■ 3. In § 660.12, add paragraph (a)(15) to
read as follows:
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14:36 Nov 17, 2015
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§ 660.12
General groundfish prohibitions.
*
*
*
*
*
(a) * * *
(15) Fail to comply with the
requirements of the Seabird Avoidance
Program described in § 660.21 when
commercial fishing for groundfish using
bottom longline gear.
*
*
*
*
*
■ 4. Add § 660.21 to read as follows:
§ 660.21
Seabird Avoidance Program.
This section contains the
requirements of the Seabird Avoidance
Program.
(a) Purpose. The purpose of the
Seabird Avoidance Program is to
minimize interactions between fishing
gear and seabird species, including
short-tailed albatross (Phoebastria
albatrus).
(b) Applicability. The requirements
specified in paragraph (c) of this section
apply to the following fishing vessels:
(1) Vessels greater than or equal to 55
ft (16.8 m) LOA engaged in commercial
fishing for groundfish with bottom
longline gear as defined in § 660.11
pursuant to the gear switching
provisions of the Limited Entry Trawl
Fishery, Shorebased IFQ Program as
specified in § 660.140(k), or pursuant to
Subparts E or F of this Part, except as
provided in paragraph (b)(2) of this
section.
(2) Exemptions. The requirements
specified in paragraph (c) of this section
do not apply to Pacific Coast treaty
Indian fisheries, as described at
§ 660.50, or to anglers engaged in
recreational fishing for groundfish, as
described in Subpart G of this Part.
(c) Seabird Avoidance
Requirements—(1) General
Requirements. The operator of a vessel
described in paragraph (b)(1) of this
section must:
(i) Gear onboard. Have onboard the
vessel seabird avoidance gear as
specified in paragraph (c)(2) of this
section.
(ii) Gear inspection. Upon request by
an authorized officer or observer, make
the seabird avoidance gear available for
inspection.
(iii) Gear use. Use seabird avoidance
gear as specified in paragraph (c)(2) of
this section that meets the standards
specified in paragraph (c)(3) of this
section while bottom longline and snap
gears are being deployed.
(iv) Handling of hooked short-tailed
albatross.
(A) Safe release of live short-tailed
albatross. Make every reasonable effort
to ensure short-tailed albatross brought
on board alive are released alive and
that, whenever possible, hooks are
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Fmt 4700
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removed without jeopardizing the life of
the bird(s). If the vessel operator
determines, based on personal
judgment, that an injured bird is likely
to die upon release, the vessel operator
is encouraged to seek veterinary care in
port. Final disposition of an injured bird
will be with a Wildlife Rehabilitator. If
needed, phone the U.S. Fish and
Wildlife Service at 503–231–6179 to
assist in locating a qualified Wildlife
Rehabilitator to care for the short-tailed
albatross.
(B) Dead short-tailed albatross must
be kept as cold as practicable while the
vessel is at sea and frozen as soon as
practicable upon return to port.
Carcasses must be labeled with the
name of vessel, location of hooking in
latitude and longitude, and the number
and color of any leg band if present on
the bird. Leg bands must be left attached
to the bird. Phone the U.S. Fish and
Wildlife Service at 503–231–6179 to
arrange for the disposition of dead
short-tailed albatross.
(C) All hooked short-tailed albatross
must be reported to U.S. Fish and
Wildlife Service Law Enforcement by
the vessel operator by phoning 360–
753–7764 (WA); 503–682–6131 (OR); or
916–414–6660 (CA) as soon as
practicable upon the vessel’s return to
port.
(D) If a NMFS observer is on board at
the time of a hooking event, the observer
shall be responsible for the disposition
of any captured short-tailed albatross
and for reporting to U.S. Fish and
Wildlife Service Law Enforcement
Otherwise, the vessel operator shall be
responsible.
(2) Gear Requirements. The operator
of a vessel identified in paragraph (b)(1)
of this section must comply with the
following gear requirements:
(i) Snap gear. Vessels using snap gear
as defined at § 660.11 must deploy a
minimum of a single streamer line in
accordance with the requirements of
paragraphs (c)(3)(i) through (ii) of this
section, except as provided in paragraph
(c)(2)(iii) of this section.
(ii) Bottom longline. Vessels using
bottom longline gear must deploy
streamer lines in accordance with the
requirements of paragraphs (c)(3)(i) and
(iii) of this section, except as provided
in paragraph (c)(2)(iii) of this section.
(iii) Weather Safety Exemption.
Vessels are exempted from the
requirements of paragraph (c)(1)(iii) of
this section when a National Weather
Service Gale Warning is in effect. This
exemption applies only during the time
and within the area indicated in the
National Weather Service Gale Warning.
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(3) Gear performance and material
standards. (i) Material standards for all
streamer lines. All streamer lines must:
(A) Have streamers spaced a
maximum of every 16 ft 5 in (5 m).
(B) Have individual streamers that
hang attached to the mainline to 10 in
(0.25 m) above the waterline in the
absence of wind.
(C) Have streamers constructed of
material that is brightly colored, UVprotected plastic tubing or 3/8 inch
polyester line or material of an
equivalent density.
(ii) Snap gear streamer line standards.
For vessels using snap gear, a streamer
line must:
(A) Be a minimum length of 147 ft 7
in (45 m).
(B) Be deployed so that streamers are
in the air a minimum of 65 ft 7 in (20
m) aft of the stern and within 6 ft 7 in
(2 m) horizontally of the point where
the main groundline enters the water
before the first hook is set.
(iii) Bottom longline streamer line
standards. Vessels using bottom
longline gear but not snap gear must use
paired streamer lines meeting the
following requirements:
(A) Streamer lines must be a
minimum length of 300 feet (91.4 m).
(B) Streamer lines must be deployed
so that streamers are in the air a
minimum of 131 ft (40m) aft of the stern
for vessels under 100 ft (30.5 m) LOA
and 197 ft (60m) aft of the stern for
vessels 100 ft (30.5 m) or over.
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14:36 Nov 17, 2015
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(C) At least one streamer line must be
deployed in accordance with paragraph
(c)(3)(iii)(B) before the first hook is set
and a second streamer line must be
deployed within 90 seconds thereafter.
(D) For vessels deploying bottom
longline gear from the stern, the
streamer lines must be deployed from
the stern, one on each side of the main
groundline.
(E) For vessels deploying bottom
longline gear from the side, the streamer
lines must be deployed from the stern,
one over the main groundline and the
other on one side of the main
groundline.
■ 5. In § 660.140, revise paragraph
(k)(1)(iv) to read as follows:
§ 660.140
Shorebased IFQ Program.
*
*
*
*
*
(k) * * *
(1) * * *
(iv) The vessel must comply with
prohibitions applicable to the limited
entry fixed gear fishery as specified at
§ 660.212, gear restrictions applicable to
limited entry fixed gear as specified in
§§ 660.219 and 660.230(b), and
management measures specified in
§ 660.230(d), including restrictions on
the fixed gear allowed onboard, its
usage, and applicable fixed gear
groundfish conservation area
restrictions, except that the vessel will
not be subject to limited entry fixed gear
trip limits when fishing in the
Shorebased IFQ Program. Vessels using
bottom longline and snap gears as
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71981
defined at § 660.11 are subject to the
requirements of the Seabird Avoidance
Program described in § 660.21.
*
*
*
*
*
■ 6. In § 660.230, add paragraph (b)(5) to
read as follows:
§ 660.230 Fixed gear fishery-management
measures.
*
*
*
*
*
(b) * * *
(5) Vessels fishing with bottom
longline and snap gears as defined at
§ 660.11 are subject to the requirements
of the Seabird Avoidance Program
described in § 660.21.
*
*
*
*
*
■ 7. In § 660.330, revise paragraph
(b)(2)(i) to read as follows:
§ 660.330 Open access fisherymanagement measures.
*
*
*
*
*
(b) * * *
(2) * * *
(i) Fixed gear (longline, trap or pot, set
net and stationary hook-and-line gear,
including commercial vertical hookand-line gear) must be attended at least
once every 7 days. Vessels fishing with
bottom longline and snap gears as
defined at § 660.11 are subject to the
requirements of the Seabird Avoidance
Program described in § 660.21.
*
*
*
*
*
[FR Doc. 2015–29249 Filed 11–17–15; 8:45 am]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 80, Number 222 (Wednesday, November 18, 2015)]
[Rules and Regulations]
[Pages 71975-71981]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2015-29249]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 660
[Docket No. 140214140-5999-01]
RIN 0648-BD92
Fisheries Off West Coast States; Pacific Coast Groundfish
Fishery; Seabird Avoidance Measures
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This final rule implements a Seabird Avoidance Program in the
Pacific Coast Groundfish Fishery. The rule was recommended by the
Pacific Fishery Management Council (Council) in November 2013 to
minimize the take of ESA-listed short-tailed albatross (Phoebastria
albatrus). A 2012 U.S. Fish and Wildlife Service (USFWS) Biological
Opinion (Opinion) required NMFS to initiate implementation of
regulations within 2 years that mandate the use of seabird avoidance
measures by vessels greater than or equal to 55 feet length overall
(LOA) using bottom longline gear to harvest groundfish. The seabird
avoidance measures, including streamer lines that deter birds from
ingesting baited hooks, are modeled after a similar regulatory program
in effect for the Alaskan groundfish fishery.
DATES: Effective on December 18, 2015.
ADDRESSES: Information relevant to this final rule, which includes a
final environmental assessment (EA), are available from William W.
Stelle, Jr., Regional Administrator, West Coast Region, NMFS, 7600 Sand
Point Way NE., Seattle, WA 98115-0070. Electronic copies of this final
rule are also available at the NMFS West Coast Region Web site: https://www.westcoast.fisheries.noaa.gov.
FOR FURTHER INFORMATION CONTACT: Sarah Williams, 206-526-4646; (fax)
206-526-6736; sarah.williams@noaa.gov.
SUPPLEMENTARY INFORMATION:
Background
The purpose of this rule is to reduce interactions between ESA-
listed seabirds and groundfish longline gear. This final rule amends
the regulations governing the Pacific Coast Groundfish Fishery
(fishery) to require seabird avoidance measures--specifically, the use
of streamer lines and related provisions similar to those currently
mandated in the Alaskan groundfish fishery--by vessels 55 ft LOA or
greater in the bottom longline fishery.
This rule is needed to minimize takes of endangered short-tailed
albatross and comply with a 2012 Biological Opinion (Opinion) issued by
the U.S. Fish and Wildlife Service.
In sum, the rule:
Requires the use of streamer lines in the commercial
longline fishery of the Pacific Coast Groundfish Fishery for non-tribal
vessels 55 feet in length or greater;
Requires vessels to deploy one or two streamer lines
depending on the type of longline gear being set;
Requires that streamer lines meet technical specifications
and be available for inspection; and
Allows for a rough weather exemption from using streamer
lines for safety purposes. The threshold for the rough weather
exemption is a Gale Warning as issued by the National Weather Service.
The rule is designed to be consistent with the requirements of the
Opinion and responsive to issues raised through the public process and
consultation with experts.
Comments and Responses
NMFS solicited public comment on the proposed seabird avoidance
measures (79 FR 53401, September 9, 2014). The comment period ended
October 9, 2014. NMFS received seven comment letters from individuals
or organizations. The letters are available in their entirety from NMFS
(see
[[Page 71976]]
ADDRESSES) or at the following web address: https://www.regulations.gov/#!docketBrowser;rpp=25;po=0;dct=PS;D=NOAA-NMFS-2014-0099. For clarity
in responding, comments have been organized into the following
categories, which are addressed in turn below: Monitoring, Gear
Specification and Performance, Scope, Environmental Assessment, and
Other.
Monitoring
Comment 1: Observers or Electronic Monitoring should be used to
monitor compliance with performance and materials standards in order
for the seabird avoidance regulations to be effective.
Response: NMFS agrees. The West Coast Groundfish Observer Program
(WCGOP) developed and implemented a sampling protocol in 2009 and 2010
to characterize the longline fleet and its use of seabird avoidance
gear. The protocol was designed to provide data on the types of
streamer lines being deployed and the performance of the streamers
insofar as it can be determined visually. For example, observers
recorded the number of streamer lines deployed; where the streamer
lines were deployed relative to sinking hooks; the deployment of towed
objects on the end of streamer lines; the extent of streamer lines
relative to the water surface; the number of streamers on each line;
the color and material of the streamers; the distance between
streamers; the distance from the stern to the first streamer; and a
range of measurements associated with the design and performance of
streamer lines. The information can be used by managers to assess the
performance of streamer lines at sea. Observers currently record the
type of seabird avoidance gear being used. In 2015, this will include a
distinction between single and double streamer lines. Observers also
record the catch of seabirds which is the ultimate determinant of the
performance of seabird avoidance measures. In response to this comment
and the ongoing need to characterize the use of seabird avoidance gear,
WCGOP will refine the sampling protocol for implementation in 2016 or
earlier as opportunity allows.
Comment 2: NMFS should use either human observers or electronic
means to monitor seabird interactions in the at-sea hake fishery
because there is a high overlap of fishing areas with albatross
occurrence; and, the fleet's practice of continuous offal discharge may
attract birds. It is known that bird strikes with trawl cables cause
high mortality of albatross in other regions.
Response: As described in the BiOp, seabirds are attracted to offal
plumes and can strike trawl cables, sonar cables, or become entangled
on nets at or near the surface. Such interactions are unlikely to be
detected as they do not show up on the deck to be sampled under normal
observer protocols. NMFS agrees with the need to characterize seabird
mortality in the at-sea hake fishery and is committed to developing a
monitoring plan; however, there are significant issues associated with
both the observer program and electronic monitoring that make it
premature to choose a specific course of action at this time.
Regarding the observer program, observer duties are carefully
prescribed according to priorities developed to support fishery
management decisions. The main priority is to monitor catch
composition--including seabirds that come up with the trawl. Each
processing vessel carries two observers. Observers subsample the catch
to collect data used to estimate catch composition. In addition, the
observers collect biological data from groundfish, protected species
including seabirds, and prohibited species. Observers are required to
be in the factory, below deck, for the majority of their sampling.
Observation of trawl and sonar cables would occur on deck and take a
significant amount of time away from catch composition sampling.
Electronic monitoring is in a developmental stage for West Coast
groundfish fisheries and significant research is necessary before it is
practicable to apply to seabird monitoring in the at-sea hake fishery.
Similar to observers, electronic monitoring is being developed to
monitor catch composition. There have not been formal investigations
into the effectiveness and practicability of training cameras away from
the deck to monitor trawl and sonar cables.
NMFS will pursue a monitoring plan by working through the Council
and its appropriate committees, such as the Council's ESA Working Group
that was established specifically to implement the Opinion; and, ad hoc
committees composed to advise the Council on the development of
electronic monitoring. Such committees offer a formal opportunity to
engage the Council in monitoring and conservation issues and is the
most appropriate opportunity to develop an effective and practicable
monitoring plan.
Comment 3: Observers should record wind speed to associate weather
data with seabird interactions in order to assess impacts associated
with the rough weather exemption.
Response: NMFS agrees. Observers currently record weather
conditions using the Beaufort scale for any sighting or take of an ESA-
listed species, including short-tailed albatross. Weather observations
are currently made at the time the observer encounters the animal
which, in longline fisheries, is usually during the retrieval of gear.
The weather conditions during retrieval may be different from when the
mortality event occurred, which is typically as gear is being set. For
this reason, and in response to this comment, NMFS will modify WCGOP
sampling protocols so that observers record weather conditions as
longlines are being set for at least a subset of hauls. The modified
protocol may not be fully effective until 2016 due to program
logistics.
Comment 4: NMFS should monitor the free streamer line program to
determine if lines are being used properly, ensure plastic components
of the streamer lines are not illegally discarded at sea, and to avoid
wasteful spending of U.S. tax dollars that are funding the program.
Response: NMFS agrees. Consistent with the response to Comment 1
above, observers are monitoring the performance of streamer lines at
sea. Observers also monitor for violations of the International
Convention for the Prevention of Pollution from Ships (MARPOL) that
prohibits the at-sea disposal of all plastics. Observers document
compliance infractions and suspected violations in their logbook and
complete a written statement during debriefing.
Gear Specification and Performance
Comment 5: NMFS should exempt the requirement to use streamer lines
during longline sets that take place at night. Based on 20 years of
personal experience, I have never encountered a seabird on a night set.
Requiring streamer lines during night sets imposes a safety risk and
inconvenience without reducing seabird mortality.
Response: To address this comment, NMFS conducted an analysis to
determine if seabird catch rates differ when the longline gear is set
in the dark versus the light. The analysis shows a reduction in the
seabird bycatch when the gear is set at night and could provide an
option for fishermen to not use streamer lines at night in the future.
At this time, NMFS has determined that providing a night-setting
exemption is outside the scope of the proposed rule. NMFS received
comments from the Council on including an exemption for night setting,
including comments from the U.S. Coast Guard representative,
[[Page 71977]]
which supported the exemption but requested further investigation into
an exemption rather than inclusion in the regulations at this time.
Comment 6: The proposed rule is inadequate and ineffective as a
seabird bycatch mitigation measure. Best practices, as adopted by the
Agreement on the Conservation of Albatrosses and Petrels (ACAP), do not
support only using streamer lines to deter seabirds. Streamer lines
should be used in conjunction with other measures such as weighting the
line to maximize sink rates; actively deterring birds from baited hooks
by using bird scaring lines; and, setting at night.
Response: NMFS disagrees that the proposed rule is inadequate;
however, NMFS agrees that the full range of best practices described by
ACAP is an important component of effective seabird conservation. NMFS
and the Council considered alternatives that would have implemented the
full suite of ACAP best practices in the EA (see ADDRESSES). The
measures described in the comment (other than streamer lines) are being
pursued by non-regulatory means. NMFS and partner organizations are
working with fishermen to encourage voluntary implementation of
measures consistent with ACAP best practices, including sinking hooks
quickly, night setting, and managing discharge of offal and bait.
Fishermen on the West Coast have a significant incentive to avoid
seabirds in order to ensure baited hooks are available to catch fish. A
hook with a seabird on it precludes that opportunity and impacts the
profitability of fishing operations. For this reason and as analyzed in
the EA, NMFS and the Council determined that a non-regulatory approach
to the full suite of best practices was the most appropriate at this
time. This does not preclude regulatory approaches in the future should
monitoring indicate that voluntary efforts are not sufficient. To that
end, NMFS has worked to establish the ESA Working Group to consider new
information and formulate advice on adaptive management to the Council.
Comment 7: The proposed streamer line specifications are inadequate
and ineffective. The specifications used under the Convention on the
Conservation of Antarctic Marine Living Resources (CCAMLR) should be
adopted, including: (1) Minimum of height at stern of 7 m; (2) minimum
streamer line length of 150 m and the use of a drogue; (3) no rough
weather exemption; and, (4) the aerial extent of streamer lines should
be stipulated as a performance standard (100 m is suggested).
Response: NMFS disagrees that the proposed streamer line
specifications are inadequate and ineffective. The CCAMLR regulations
reflect the development of seabird avoidance measures designed for the
specific fisheries and seabird assemblages. The sub-Antarctic fisheries
governed under CCAMLR include primarily Patagonia toothfish
(Dissostichus eleginoides), which is fished with the Spanish method of
bottom longlining, where the gear is more buoyant than that used on the
West Coast. The majority of the vessels are large (30-50 m) and deploy
gear from the stern at speeds of 10-13 knots. The prevalent seabirds
incidentally taken are albatrosses and petrels species, many of which
dive to foraging depths that are substantially deeper than the North
Pacific albatross and other species that occur off the West Coast.
In contrast, West Coast groundfish fisheries target primarily
sablefish, which is a demersal species fished with bottom gear
consisting of groundlines to which relatively short gangions are
attached. In general, vessels deploy gear from the stern. The prevalent
seabird species incidentally taken are fulmars, gulls, and albatrosses.
The CCAMLR streamer line specifications are designed to provide
more aerial coverage than is necessary or appropriate for West Coast
groundfish fisheries. The minimum stern height, line length, and aerial
extent specifications cover a greater area because longlines used in
those fisheries are more buoyant and extend further behind the vessel
than occurs in fisheries covered under this rule, and because the
seabird species taken in CCAMLR fisheries dive to deeper depths than
those on the West Coast. The specifications in this rule were
recommended based on extensive research that demonstrated them to be
effective in Alaskan groundfish fisheries, where the targeted fish
species, vessels, and seabirds are similar and, in some cases,
identical. More information on this research and the effectiveness of
the streamer line specification in this final rule is available in the
Opinion or EA (see ADDRESSES).
NMFS notes however that preliminary research by Washington Sea
Grant indicates that some vessels in West Coast groundfish fisheries
are using floats on gangions to avoid predation by non-marketable
bottom fish (i.e., hagfish). The floats may reduce the effectiveness of
these streamer line specifications by keeping baited hooks in the water
column past the extent of streamer lines. It is unclear at this time
how widespread the use of floats is, how much it influences seabird
catch rates, and what alternatives are appropriate if floats are
determined to be a significant issue affecting seabird catch rates.
Because the research is preliminary, and because the streamer line
specifications in this final rule have been demonstrated to be
effective in reducing seabird mortality and are required by the
Opinion, NMFS is finalizing this rule and will continue to monitor its
effectiveness to determine if future changes are warranted. NMFS is
also continuing to support Washington Sea Grant in conducting this
research and has worked to establish the ESA Working Group to consider
new information and formulate advice on adaptive management to the
Council.
Comment 8: Vessels should not be permitted to take excessive
numbers of seabirds. Vessels should be required to move to night
setting for the remainder of the fishing season if seabird bycatch
exceeds 0.01 seabirds per 1000 hooks in a set, or until the vessel is
able to demonstrate a line sink rate of a minimum of 0.3 m/second to 15
m depth. Applying a performance standard quickly halts lax and
ineffective fishing practices.
Response: A system does not currently exist within NMFS to hold
individual vessels accountable for seabird mortality in real time.
Similarly, it is not feasible for NMFS to monitor and enforce sink
rates of longline gear on individual vessels. More importantly, NMFS
does not believe such a system is necessary given that the final
regulations are designed to effectively reduce seabird bycatch in the
fleet where most of the seabirds are taken.
Scope of the Regulations
Comment 9: Vessels smaller than 55 ft should be required to use
seabird avoidance measures to minimize the chance that such vessels
will take ESA-listed short-tailed albatross and other seabirds.
Response: NMFS agrees that there may be a risk to short-tailed
albatross from longline vessels under 55 ft; however, it would be
premature to require that they use seabird avoidance gear at this time.
The Opinion specifies that this rule apply to larger vessels for the
following reasons: (1) Vessels under 55 ft have not been observed to
interact with short-tailed albatross; (2) vessels under 55 ft are being
encouraged through formal outreach described in the EA (see ADDRESSES)
to deploy seabird avoidance measures on a voluntary basis; and, (3)
NMFS does not have an appropriate technical
[[Page 71978]]
specification for streamer lines proven to be safe for smaller vessels.
To address the latter, Washington Sea Grant is conducting research to
determine safe and effective seabird avoidance measures for vessels
under 55 ft. In limiting the requirement specified in the Opinion to
vessels 55 ft and over, USFWS further required NMFS to adapt management
as appropriate in response to that research and ongoing monitoring.
NMFS is committed to review new information as it becomes available to
determine if these regulations should be adapted to cover smaller
vessels. To that end, NMFS has worked to establish the ESA Working
Group to consider new information and formulate advice on adaptive
management to the Council.
Comment 10: NMFS should require that seabird avoidance measures be
deployed in the at-sea hake fishery because there is a high overlap of
fishing areas with albatross occurrence and the fleet's practice of
continuous offal discharge that may attract birds. It is known that
bird strikes with trawl cables cause high mortality of albatross in
other regions.
Response: NMFS agrees that there is a potential threat to seabirds
associated with the at-sea hake fishery; however, it is premature to
regulate that fishery at this time. As described in the response to
Comment 2 above, NMFS will pursue a monitoring plan to assess the level
of threat and appropriate responses. Regulating the at-sea hake fishery
is outside the scope of this rule, which is focused on implementing
requirements stipulated by USFWS in the Opinion. USFWS recognized the
potential for interaction between seabirds and the at-sea hake fishery
but determined that the focus of seabird avoidance measures should be
the longline fleet. In doing so, USFWS further required NMFS to adapt
management as appropriate in response to new information. NMFS is
committed to reviewing new information as it becomes available to
determine if these regulations should be adapted to other fisheries
such as the at-sea hake fishery. To that end, NMFS has worked to
establish the ESA Working Group to consider new information and
formulate advice on adaptive management to the Council.
Environmental Assessment
Comment 11: The EA must analyze whether short-tailed albatross are
at higher risk of entanglement during high wind events.
Response: NMFS agrees. The EA, in Section 4.1.1, acknowledges the
uncertainty regarding seabird behavior during rough weather and
concludes the exemption is not expected to significantly influence the
overall reduction in seabird bycatch. NMFS is not aware of additional
information pertinent to assessing the effects of rough weather on
seabird encounters by longline vessels but will continue to monitor
observer data and adapt management as new information becomes
available. To that end, NMFS has worked to establish the ESA Working
Group to consider new information and formulate advice on adaptive
management to the Council.
Comment 12: The EA does not adequately assess the effects of
vessels under 55 ft on short-tailed albatross.
Response: NMFS disagrees. Consistent with the response to Comment
9, the EA acknowledges there may be a risk to short-tailed albatross
from vessels under 55 ft and incorporates voluntary conservation and
ongoing research into analysis of the status quo alternative (See
ADDRESSES).
Other
Comment 13: The groundfish fishery operates in important seabird
foraging habitat as well as critical habitat of leatherback sea turtles
and green sturgeon. Streamer lines may have unintended consequences if
they are lost overboard. Streamers should be made of plant-based
materials in order to minimize the biological risks associated with
ingestion by marine animals.
Response: In response to this comment, NMFS consulted with NOAA's
Marine Debris Program to determine if there is evidence for streamer
lines as marine debris in areas such as Alaska and Hawaii, where there
are existing requirements for longline vessels to use them. Streamers
(the plastic component of streamer lines) have been observed during
shoreline clean-ups in Alaska; however, the quantity relative to other
marine debris is very low. Reports from shoreline cleanups in Hawaii
have not noted the presence of streamers. Given the low incidence of
observed streamers, it would not be reasonable to change design
specifications at this time. Streamer lines are constructed of
materials, including plastics, sufficient to withstand at-sea
conditions. A change in the material specifications would require
significant research to ensure streamer lines would continue to
function by reducing seabird entanglement. Such research is not
practicable at this time. NMFS notes that intentional disposal at sea
is unlikely because fishermen are subject to MARPOL, which prohibits
the at-sea disposal of plastics.
Comment 14: NMFS should ensure authorization of fisheries complies
with the Migratory Bird Treaty Act (MBTA).
Response: NMFS agrees. The final regulations are consistent with
the MBTA.
Comment 15: NMFS should provide, and crewmembers should be required
to attend, workshops to identify and distinguish short-tailed albatross
from other albatrosses and also to safely release live short-tailed
albatrosses.
Response: NMFS agrees that education and outreach is an important
component of seabird conservation; however, NMFS disagrees that it
should be required. NMFS has provided funding for Washington Sea Grant
to conduct outreach that has included mailings to all fixed-gear permit
holders, port meetings with fishermen, an internet site, and
educational exhibits at trade shows. The material includes information
on seabird avoidance, species identification, and how to handle hooked
albatross. NMFS believes that these efforts have been successful in
educating fishermen on issues related to seabird bycatch.
Comment 16: A number of commenters were in support of the proposed
regulations.
Response: NMFS acknowledges this comment.
Changes from the Proposed Rule
There are no substantial changes from the proposed rule. NMFS made
one modification to re-locate the regulatory text so that it is grouped
with other groundfish regulations. The goal of this change is to locate
the seabird avoidance program regulations near other programs that
apply to multiple sectors of the groundfish fishery.
Classification
Pursuant to section 304(b)(1)(A) of the MSA, the NMFS Assistant
Administrator has determined that this final rule is consistent with
the Pacific Coast Groundfish FMP, other provisions of the MSA, and
other applicable law.
NMFS and the Council prepared a final Environmental Assessment (EA)
for this regulation and concluded that there would not be a significant
impact on the human environment as a result of this rule. A copy of the
EA is available from NMFS (see ADDRESSES).
This final rule has been determined to be not significant for
purposes of Executive Order 12866.
The Regulatory Flexibility Act requires Federal agencies to conduct
a full RFAA unless the agency can certify that the proposed and/or
final rule would not have a significant economic
[[Page 71979]]
impact on a substantial number of small entities.
The Chief Counsel for Regulation of the Department of Commerce
certified to the Chief Counsel for Advocacy of the Small Business
Administration during the proposed rule stage that this action would
not have a significant economic impact on a substantial number of small
entities. The factual basis for the certification was published in the
proposed rule and is not repeated here. No comments were received
regarding this certification. As a result, a regulatory flexibility
analysis was not required and none was prepared.
Section 212 of the Small Business Regulatory Enforcement Fairness
Act of 1996 states that, for each rule or group of related rules for
which an agency is required to prepare a FRFA, the agency shall publish
one or more guides to assist small entities in complying with the rule,
and shall designate such publications as ``small entity compliance
guides.'' The agency shall explain the actions a small entity is
required to take to comply with a rule or group of rules. As part of
this rulemaking process, a public notice that also serves as small
entity compliance guide (the guide) was prepared. Copies of this final
rule are available from the West Coast Regional Office, and the guide
will be posted on the NMFS West Coast Region Web site and emailed to
the groundfish fishery listserve. The guide and this final rule will be
available upon request.
NMFS issued Biological Opinions under the Endangered Species Act
(ESA) on August 10, 1990, November 26, 1991, August 28, 1992, September
27, 1993, May 14, 1996, and December 15, 1999, pertaining to the
effects of the Groundfish FMP fisheries on Chinook salmon (Puget Sound,
Snake River spring/summer, Snake River fall, upper Columbia River
spring, lower Columbia River, upper Willamette River, Sacramento River
winter, Central Valley spring, California coastal), coho salmon
(Central California coastal, southern Oregon/northern California
coastal), chum salmon (Hood Canal summer, Columbia River), sockeye
salmon (Snake River, Ozette Lake), and steelhead (upper, middle and
lower Columbia River, Snake River Basin, upper Willamette River,
central California coast, California Central Valley, south/central
California, northern California, southern California). These biological
opinions have concluded that implementation of the FMP is not expected
to jeopardize the continued existence of any endangered or threatened
species under the jurisdiction of NMFS, or result in the destruction or
adverse modification of critical habitat.
NMFS issued a Supplemental Biological Opinion on March 11, 2006,
concluding that neither the higher observed bycatch of Chinook in the
2005 whiting fishery nor new data regarding salmon bycatch in the
groundfish bottom trawl fishery required a reconsideration of its prior
``no jeopardy'' conclusion. NMFS also reaffirmed its prior
determination that implementation of the FMP is not likely to
jeopardize the continued existence of any of the affected ESUs. Lower
Columbia River coho (70 FR 37160, June 28, 2005) and Oregon Coastal
coho (73 FR 7816, February 11, 2008) were relisted as threatened under
the ESA. The 1999 biological opinion concluded that the bycatch of
salmonids in the Pacific whiting fishery were almost entirely Chinook
salmon, with little or no bycatch of coho, chum, sockeye, and
steelhead.
On December 7, 2012, NMFS completed a biological opinion concluding
that the groundfish fishery is not likely to jeopardize non-salmonid
marine species including listed eulachon, green sturgeon, humpback
whales, Steller sea lions, and leatherback sea turtles. The opinion
also concluded that the fishery is not likely to adversely modify
critical habitat for green sturgeon and leatherback sea turtles. An
analysis included in the same document as the opinion concluded that
the fishery is not likely to adversely affect green sea turtles, olive
ridley sea turtles, loggerhead sea turtles, sei whales, North Pacific
right whales, blue whales, fin whales, sperm whales, Southern Resident
killer whales, Guadalupe fur seals, or the critical habitat for Steller
sea lions.
West Coast pot fisheries for sablefish are considered Category II
fisheries under the Marine Mammal Protection Act (MMPA), indicating
occasional interactions. All other West Coast groundfish fisheries,
including the trawl fishery, are considered Category III fisheries
under the MMPA, indicating a remote likelihood of or no known serious
injuries or mortalities to marine mammals. MMPA section 101(a)(5)(E)
requires that NMFS authorize the taking of ESA-listed marine mammals
incidental to U.S. commercial fisheries if it makes the requisite
findings, including a finding that the incidental mortality and serious
injury from commercial fisheries will have a negligible impact on the
affected species or stock. As noted above, NMFS concluded in its
biological opinion for the 2012 groundfish fisheries that these
fisheries were not likely to jeopardize Steller sea lions or humpback
whales. The eastern distinct population segment of Steller sea lions
was delisted under the ESA on November 4, 2013 (78 FR 66140). On
September 4, 2013, based on its negligible impact determination dated
August 28, 2013, NMFS issued a permit for a period of 3 years to
authorize the incidental taking of humpback whales by the sablefish pot
fishery (78 FR 54553).
NMFS has reinitiated section 7 consultation on the Pacific Coast
Groundfish FMP with respect to its effects on listed salmonids. In the
event the consultation identifies either reasonable and prudent
alternatives to address jeopardy concerns, or reasonable and prudent
measures to minimize incidental take, NMFS would coordinate with the
Council to put additional alternatives or measures into place, as
required. After reviewing the available information, NMFS has concluded
that, consistent with sections 7(a)(2) and 7(d) of the ESA, this action
will not jeopardize any listed species, would not adversely modify any
designated critical habitat, and will not result in any irreversible or
irretrievable commitment of resources that would have the effect of
foreclosing the formulation or implementation of any reasonable and
prudent alternative measures.
On November 21, 2012, the U.S. Fish and Wildlife Service (FWS)
issued a biological opinion concluding that the groundfish fishery will
not jeopardize the continued existence of the short-tailed albatross.
The 2012 Opinion evaluated the risks of continued operation of the
Pacific Coast groundfish fishery on ESA-listed seabirds, including
short-tailed albatross. The 2012 Opinion included a Term and Condition
requiring NMFS to promulgate regulations mandating the use of streamer
lines by longline vessels 55 feet LOA or greater, patterned on the
Alaska streamer line regulations. Accordingly, for the fishery to be
exempt from the ESA section 9 prohibition regarding take of a listed
species, NMFS must initiate implementation of streamer line regulations
by November 21, 2014. The 2012 Opinion anticipates the yearly average
take of one short-tailed albatross killed from longline hooks or trawl
cables. As the short-tailed albatross population is expanding, it is
expected to result in more interactions with the Pacific Coast
Groundfish Fisheries. This action would implement one of the Terms and
Conditions of the 2012 Opinion and reduce the risk of exceeding the
take limits of short-tailed albatross, which in turn would reduce
[[Page 71980]]
the risk of economic harm to the fishing industry that could result
from the incidental take limit being exceeded. The FWS also concurred
that the fishery is not likely to adversely affect the marbled
murrelet, California least tern, southern sea otter, bull trout, or
bull trout critical habitat.
This final rule does not contain a collection-of-information
requirement subject to review and approval by OMB under the Paperwork
Reduction Act (PRA).
This final rule was developed after meaningful collaboration,
through the Council process, with the tribal representative on the
Council. The regulations have no direct effect on the tribes and were
deemed by the Council as ``necessary or appropriate'' to implement the
FMP as amended.
List of Subjects in 50 CFR Part 660
Administrative practice and procedure, American Samoa, Fisheries,
Fishing, Guam, Hawaiian natives, Indians, Northern Mariana Islands,
Reporting and recordkeeping requirements.
Dated: November 10, 2015.
Samuel D. Rauch III,
Deputy Assistant Administrator for Regulatory Programs, National Marine
Fisheries Service.
For the reasons stated in the preamble, 50 CFR part 660 is amended
as follows:
PART 660--FISHERIES OFF WEST COAST STATES
0
1. The authority citation for part 660 continues to read as follows:
Authority: 16 U.S.C. 1801 et seq., 16 U.S.C. 773 et seq., and
16 U.S.C. 7001 et seq.
0
2. In Sec. 660.11, add paragraph (6)(i)(A) and reserved paragraph
(6)(i)(B) to the definition of ``Fishing gear'' and add the definition
for ``Seabird'' in alphabetical order to read as follows:
Sec. 660.11 General definitions.
* * * * *
Fishing gear * * *
(6) * * *
(i) * * *
(A) Snap gear means a type of bottom longline gear where the hook
and gangion are attached to the groundline using a mechanical fastener
or snap.
(B) [Reserved]
* * * * *
Seabird means those bird species that habitually obtain their food
from the sea below the low water mark.
* * * * *
0
3. In Sec. 660.12, add paragraph (a)(15) to read as follows:
Sec. 660.12 General groundfish prohibitions.
* * * * *
(a) * * *
(15) Fail to comply with the requirements of the Seabird Avoidance
Program described in Sec. 660.21 when commercial fishing for
groundfish using bottom longline gear.
* * * * *
0
4. Add Sec. 660.21 to read as follows:
Sec. 660.21 Seabird Avoidance Program.
This section contains the requirements of the Seabird Avoidance
Program.
(a) Purpose. The purpose of the Seabird Avoidance Program is to
minimize interactions between fishing gear and seabird species,
including short-tailed albatross (Phoebastria albatrus).
(b) Applicability. The requirements specified in paragraph (c) of
this section apply to the following fishing vessels:
(1) Vessels greater than or equal to 55 ft (16.8 m) LOA engaged in
commercial fishing for groundfish with bottom longline gear as defined
in Sec. 660.11 pursuant to the gear switching provisions of the
Limited Entry Trawl Fishery, Shorebased IFQ Program as specified in
Sec. 660.140(k), or pursuant to Subparts E or F of this Part, except
as provided in paragraph (b)(2) of this section.
(2) Exemptions. The requirements specified in paragraph (c) of this
section do not apply to Pacific Coast treaty Indian fisheries, as
described at Sec. 660.50, or to anglers engaged in recreational
fishing for groundfish, as described in Subpart G of this Part.
(c) Seabird Avoidance Requirements--(1) General Requirements. The
operator of a vessel described in paragraph (b)(1) of this section
must:
(i) Gear onboard. Have onboard the vessel seabird avoidance gear as
specified in paragraph (c)(2) of this section.
(ii) Gear inspection. Upon request by an authorized officer or
observer, make the seabird avoidance gear available for inspection.
(iii) Gear use. Use seabird avoidance gear as specified in
paragraph (c)(2) of this section that meets the standards specified in
paragraph (c)(3) of this section while bottom longline and snap gears
are being deployed.
(iv) Handling of hooked short-tailed albatross.
(A) Safe release of live short-tailed albatross. Make every
reasonable effort to ensure short-tailed albatross brought on board
alive are released alive and that, whenever possible, hooks are removed
without jeopardizing the life of the bird(s). If the vessel operator
determines, based on personal judgment, that an injured bird is likely
to die upon release, the vessel operator is encouraged to seek
veterinary care in port. Final disposition of an injured bird will be
with a Wildlife Rehabilitator. If needed, phone the U.S. Fish and
Wildlife Service at 503-231-6179 to assist in locating a qualified
Wildlife Rehabilitator to care for the short-tailed albatross.
(B) Dead short-tailed albatross must be kept as cold as practicable
while the vessel is at sea and frozen as soon as practicable upon
return to port. Carcasses must be labeled with the name of vessel,
location of hooking in latitude and longitude, and the number and color
of any leg band if present on the bird. Leg bands must be left attached
to the bird. Phone the U.S. Fish and Wildlife Service at 503-231-6179
to arrange for the disposition of dead short-tailed albatross.
(C) All hooked short-tailed albatross must be reported to U.S. Fish
and Wildlife Service Law Enforcement by the vessel operator by phoning
360-753-7764 (WA); 503-682-6131 (OR); or 916-414-6660 (CA) as soon as
practicable upon the vessel's return to port.
(D) If a NMFS observer is on board at the time of a hooking event,
the observer shall be responsible for the disposition of any captured
short-tailed albatross and for reporting to U.S. Fish and Wildlife
Service Law Enforcement Otherwise, the vessel operator shall be
responsible.
(2) Gear Requirements. The operator of a vessel identified in
paragraph (b)(1) of this section must comply with the following gear
requirements:
(i) Snap gear. Vessels using snap gear as defined at Sec. 660.11
must deploy a minimum of a single streamer line in accordance with the
requirements of paragraphs (c)(3)(i) through (ii) of this section,
except as provided in paragraph (c)(2)(iii) of this section.
(ii) Bottom longline. Vessels using bottom longline gear must
deploy streamer lines in accordance with the requirements of paragraphs
(c)(3)(i) and (iii) of this section, except as provided in paragraph
(c)(2)(iii) of this section.
(iii) Weather Safety Exemption. Vessels are exempted from the
requirements of paragraph (c)(1)(iii) of this section when a National
Weather Service Gale Warning is in effect. This exemption applies only
during the time and within the area indicated in the National Weather
Service Gale Warning.
[[Page 71981]]
(3) Gear performance and material standards. (i) Material standards
for all streamer lines. All streamer lines must:
(A) Have streamers spaced a maximum of every 16 ft 5 in (5 m).
(B) Have individual streamers that hang attached to the mainline to
10 in (0.25 m) above the waterline in the absence of wind.
(C) Have streamers constructed of material that is brightly
colored, UV-protected plastic tubing or 3/8 inch polyester line or
material of an equivalent density.
(ii) Snap gear streamer line standards. For vessels using snap
gear, a streamer line must:
(A) Be a minimum length of 147 ft 7 in (45 m).
(B) Be deployed so that streamers are in the air a minimum of 65 ft
7 in (20 m) aft of the stern and within 6 ft 7 in (2 m) horizontally of
the point where the main groundline enters the water before the first
hook is set.
(iii) Bottom longline streamer line standards. Vessels using bottom
longline gear but not snap gear must use paired streamer lines meeting
the following requirements:
(A) Streamer lines must be a minimum length of 300 feet (91.4 m).
(B) Streamer lines must be deployed so that streamers are in the
air a minimum of 131 ft (40m) aft of the stern for vessels under 100 ft
(30.5 m) LOA and 197 ft (60m) aft of the stern for vessels 100 ft (30.5
m) or over.
(C) At least one streamer line must be deployed in accordance with
paragraph (c)(3)(iii)(B) before the first hook is set and a second
streamer line must be deployed within 90 seconds thereafter.
(D) For vessels deploying bottom longline gear from the stern, the
streamer lines must be deployed from the stern, one on each side of the
main groundline.
(E) For vessels deploying bottom longline gear from the side, the
streamer lines must be deployed from the stern, one over the main
groundline and the other on one side of the main groundline.
0
5. In Sec. 660.140, revise paragraph (k)(1)(iv) to read as follows:
Sec. 660.140 Shorebased IFQ Program.
* * * * *
(k) * * *
(1) * * *
(iv) The vessel must comply with prohibitions applicable to the
limited entry fixed gear fishery as specified at Sec. 660.212, gear
restrictions applicable to limited entry fixed gear as specified in
Sec. Sec. 660.219 and 660.230(b), and management measures specified in
Sec. 660.230(d), including restrictions on the fixed gear allowed
onboard, its usage, and applicable fixed gear groundfish conservation
area restrictions, except that the vessel will not be subject to
limited entry fixed gear trip limits when fishing in the Shorebased IFQ
Program. Vessels using bottom longline and snap gears as defined at
Sec. 660.11 are subject to the requirements of the Seabird Avoidance
Program described in Sec. 660.21.
* * * * *
0
6. In Sec. 660.230, add paragraph (b)(5) to read as follows:
Sec. 660.230 Fixed gear fishery-management measures.
* * * * *
(b) * * *
(5) Vessels fishing with bottom longline and snap gears as defined
at Sec. 660.11 are subject to the requirements of the Seabird
Avoidance Program described in Sec. 660.21.
* * * * *
0
7. In Sec. 660.330, revise paragraph (b)(2)(i) to read as follows:
Sec. 660.330 Open access fishery-management measures.
* * * * *
(b) * * *
(2) * * *
(i) Fixed gear (longline, trap or pot, set net and stationary hook-
and-line gear, including commercial vertical hook-and-line gear) must
be attended at least once every 7 days. Vessels fishing with bottom
longline and snap gears as defined at Sec. 660.11 are subject to the
requirements of the Seabird Avoidance Program described in Sec.
660.21.
* * * * *
[FR Doc. 2015-29249 Filed 11-17-15; 8:45 am]
BILLING CODE 3510-22-P