Magnuson-Stevens Act Provisions; Fisheries Off West Coast States; Pacific Coast Groundfish Fishery; 2020 Harvest Specifications for Pacific Whiting, Cowcod and Shortbelly Rockfish and 2020 Pacific Whiting Tribal Allocation, 21372-21385 [2020-08019]
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Federal Register / Vol. 85, No. 75 / Friday, April 17, 2020 / Proposed Rules
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 660
[Docket No. 200410–0109]
RIN 0648–BJ53
Magnuson-Stevens Act Provisions;
Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery; 2020
Harvest Specifications for Pacific
Whiting, Cowcod and Shortbelly
Rockfish and 2020 Pacific Whiting
Tribal Allocation
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule; request for
comments.
AGENCY:
This proposed rule would
establish 2020 harvest specifications
and management measures for Pacific
whiting, shortbelly rockfish and cowcod
taken in the U.S. exclusive economic
zone off the coasts of Washington,
Oregon and California consistent with
the Magnuson-Stevens Fishery
Conservation and Management Act, the
Pacific Whiting Act of 2006, and other
applicable laws. This rule proposes
2020 harvest specifications for Pacific
whiting including the U.S. and
coastwide Total Allowable Catch (TAC),
the 2020 tribal allocation for the Pacific
whiting fishery, allocations for three
commercial whiting sectors, and setasides for Pacific whiting research and
incidental mortality in other fisheries.
The proposed rule would also adjust the
2020 harvest specifications for
shortbelly rockfish and cowcod. The
proposed measures are intended to help
prevent overfishing, achieve optimum
yield, and ensure that management
measures are based on the best scientific
information available.
DATES: Comments on this proposed rule
must be received no later than May 4,
2020.
ADDRESSES: You may submit comments
on this document, identified by NOAA–
NMFS–2020–0027 by any of the
following methods:
• Electronic Submission: Submit all
electronic public comments via the
Federal eRulemaking Portal. Go to
www.regulations.gov/#!docketDetail;
D=NOAA-NMFS-2020-0027 click the
‘‘Comment Now!’’ icon, complete the
required fields, and enter or attach your
comments.
• Mail: Barry Thom, c/o Stacey
Miller, Sustainable Fisheries Division,
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SUMMARY:
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West Coast Region, NMFS, 1201 NE
Lloyd Blvd. Suite 1100, Portland, OR
97232.
Instructions: Comments sent by any
other method, to any other address or
individual, or received after the end of
the comment period, may not be
considered by NMFS. All comments
received are 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, address, etc.),
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).
Electronic Access
This proposed rule is accessible via
the internet at the Office of the Federal
Register website at https://
www.federalregister.gov. Background
information and documents including
an integrated analysis for this action
(Analysis), which addresses the
statutory requirements of the Magnuson
Stevens Fishery Conservation and
Management Act (Magnuson-Stevens
Act), the National Environmental Policy
Act, Presidential Executive Order
12866, and the Regulatory Flexibility
Act are available at the NMFS website
at https://www.fisheries.noaa.gov/
action/2020-harvest-specificationspacific-whiting-cowcod-and-shortbellyrockfish-and-2020-pacific and at the
Pacific Fishery Management Council’s
website at https://www.pcouncil.org/.
FOR FURTHER INFORMATION CONTACT:
Stacey Miller, phone: 503–231–6290,
and email: Stacey.Miller@noaa.gov.
SUPPLEMENTARY INFORMATION:
Background
This proposed rule includes actions
for the Pacific whiting tribal and nontribal fisheries, shortbelly rockfish and
cowcod. These actions are combined
into one proposed rule because they all
relate to establishing catch limits and
management measures for Pacific Coast
groundfish stocks in 2020. This rule
proposes determining the 2020 Pacific
whiting coastwide TAC, and
establishing the Pacific whiting U.S.
TAC based on the coastwide TAC, tribal
allocation, allocations for three
commercial whiting sectors, and setasides for research and incidental
mortality of Pacific whiting as
recommended by the Pacific Fishery
Management Council (Council);
increasing the 2020 annual catch limit
(ACL) for shortbelly rockfish; and
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eliminating the 2020 annual catch target
(ACT) and reducing the research setaside for cowcod. The allocations for
Pacific whiting would be effective until
December 31, 2020. The adjusted catch
limits for cowcod and shortbelly would
supersede those put in place for 2020
through the 2019–2020 Pacific Coast
Groundfish Biennial Harvest
Specifications and Management
Measures (83 FR 63970, December 12,
2018), and are being analyzed as part of
the 2021–2022 Pacific Coast Groundfish
Biennial Harvest Specifications and
Management Measures, which are
anticipated to be effective on January 1,
2021.
Pacific Whiting
Background on the Pacific Whiting
Agreement
The transboundary stock of Pacific
whiting is managed through the
Agreement Between the Government of
the United States of America and the
Government of Canada on Pacific Hake/
Whiting of 2003, Nov. 21, 2003, T.I.A.S.
08–625 (Agreement). The Agreement
establishes bilateral bodies to
implement its terms, including: The
Joint Management Committee (JMC),
which recommends the TAC for Pacific
whiting; the Joint Technical Committee
(JTC), which conducts the Pacific
whiting stock assessment; the Scientific
Review Group (SRG), which reviews the
stock assessment; and the Advisory
Panel (AP), which provides stakeholder
input to the JMC.
The Agreement establishes a default
harvest policy of F–40 percent, which
means a fishing mortality rate that
would reduce the spawning biomass,
calculated on a per recruit basis, to 40
percent of what it would have been in
absence of fishing mortality. The U.S.
and Canada may choose a different
fishing mortality rate if they determine
that scientific evidence demonstrates
that a different rate is necessary to
sustain the offshore Pacific whiting
resource. The Agreement also explicitly
allocates 73.88 percent of the Pacific
whiting TAC to the U.S. and 26.12
percent of the TAC to Canada.
Based on the advice from the Treaty’s
JTC, SRG, and AP, the Treaty specifies
that the JMC shall recommend to the
parties an overall Pacific whiting TAC
by March 25th of each year. In years
when the JMC does make a TAC
recommendation to the parties, NMFS
(under the delegation of authority from
the Secretary of Commerce) approves
the U.S. TAC with concurrence from the
Department of State. The U.S. TAC is
allocated into tribal and non-tribal
sectors.
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The 2020 JMC negotiations were held
from March 11–13, 2020, via the
internet, but did not result in a bilateral
agreement on the coastwide TAC. Based
on the most current information, the
stock assessment estimates a TAC of
666,458 metric tons (mt) based on the
default harvest policy. The final
Canadian proposal was 390,000 mt and
the final U.S. proposal was 555,000 mt
for the adjusted coastwide TAC. The
Agreement does not specify a procedure
for when the JMC does not agree on a
coastwide TAC. However, the 2006
Pacific Whiting Act (16 U.S.C. 7006(c))
identifies procedures for when the JMC
does not recommend a final TAC. The
Act states that NMFS (as delegated by
the Secretary of Commerce) should
establish the Pacific whiting TAC,
taking into account recommendations
from the JMC, JTC, SRG, AP, and
Council. The Act requires NMFS to base
the TAC decision on the best scientific
information available, and use the
default harvest rate unless scientific
information indicates a different rate is
necessary to sustain the Pacific whiting
resource. The Act also requires NMFS to
establish the U.S. share of the TAC
based on the U.S./Canada percentage
split and adjustments specified in the
Agreement.
2020 Pacific Whiting Stock Assessment
and Scientific Review
The JTC completed a stock assessment
for Pacific whiting in February 2020
(available at https://
www.fisheries.noaa.gov/resource/
document/2020-pacific-hake-whitingstock-assessment). The assessment
presents a model that uses an acoustic
survey biomass index, catches of the
transboundary Pacific whiting stock,
and age compositions to estimate the
biomass of the current stock. The most
recent survey, conducted collaboratively
between the Canadian Department of
Fisheries and Oceans and NMFS, was
completed in 2019. Age-composition
data from the acoustics survey and
fishery catch provide information to
estimate relative year class strength.
Pacific whiting displays high
recruitment variability relative to other
west coast groundfish stocks, and
typically an occasional large year-class
supports much of the fishery. The
Pacific whiting stock is currently
supported by multiple above average
cohorts simultaneously, including the
2010, 2014, 2016, and 2017 year classes,
which is highly unusual. The current
assessment estimates the 2010 year class
as the second highest recruitment in the
assessment time series. The 2014 and
2016 year classes are estimated to be
above average in strength and the 2017
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year is about average, however there is
high uncertainty around the strength of
these later year classes. The assessment
estimates small year classes in 2011,
2013, 2015, and 2018, and there is no
information in the data to estimate the
sizes of the 2019 and 2020 year classes.
The Pacific whiting relative spawning
stock is estimated to be 1.196 million
mt, or 65 percent of unfished levels at
the start of 2020. The estimated biomass
has declined since 2017, during a time
of record catches and as the very large
2010 year class ages and mortality
surpasses increased production.
Projections show that even in the
absence of fishing, the stock is expected
to decline from 65 percent to 62 percent
of unfished biomass.
The stock is considered healthy, and
the joint probability that the relative
spawning stock biomass is both below
40 percent of unfished level and that
fishing mortality is above the relative
fishing intensity of the Agreement’s F–
40 percent default harvest rate is
estimated to be 4.3 percent.
2020 Pacific Whiting TAC Evaluation
and Recommendation
NMFS considered information and
recommendations from the Treaty’s
JMC, JTC, SRG, AP, and the Council.
The stock assessment from the JTC and
the SRG peer review are the best
scientific information available for
determining the coastwide Pacific
whiting TAC. NMFS heard testimony
from the AP and JMC at the March 2020
meeting. The Council discussed Pacific
whiting during its April 2020 meeting
and did not make any specific
recommendations regarding the 2020
Pacific whiting TAC.
NMFS initially considered setting the
TAC resulting from the default harvest
rate (666,458 mt) and all of the potential
adjusted coastwide TACs discussed
during the AP and JMC March 2020
meeting. This includes the U.S. initial
(597,500 mt) and final positions
(555,000 mt), and the Canadian initial
(300,000 mt) and final positions
(390,000 mt). However, because
Canada’s proposed TACs are well below
the TACs that support a sustainable
whiting resource according to the stock
assessment and would have negative
economic impact on the U.S. fleet with
little economic impact on Canada’s
fleet, we excluded them from further
consideration.
NMFS therefore evaluated coastwide
TACs ranging from 555,000 mt to
666,458 mt in developing our proposed
coastwide TAC of 575,000 mt. The stock
assessment supports that most of the
TACs within this range would provide
adequate opportunity for both Canadian
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and U.S. fleets, while sustainably
managing the Pacific whiting resource.
Biological Impacts of Potential Whiting
TAC Levels
The Act directs NMFS to use the
default harvest rate set out in the
Agreement unless NMFS determines
that a different rate is necessary to
sustain the offshore whiting resource.
The Agreement specifies a default
harvest rate of ‘‘F–40 percent’’ which is
the fishing mortality rate that would
reduce the relative spawning stock
biomass, calculated on a per recruit
basis (a measure of stock reproductive
potential) to 40 percent of what it would
have been in the absence of fishing
mortality. Although there is not a
default biomass level, the JMC, since
implementation of the Agreement, has
focused on choosing a TAC designed to
prevent the relative spawning stock
biomass from falling below 40 percent
of what it would have been in the
absence of fishing mortality, often called
B40. NMFS will follow the same
practice of choosing a TAC designed to
prevent the relative spawning stock
biomass from falling below this biomass
level.
To determine the impact of a specific
TAC on relative spawning stock
biomass, we applied an estimate of the
Pacific whiting fleet’s utilization rate,
the proportion of the TAC removed
through fishing effort, to the range of
TACs we considered. Over the last ten
years, neither the U.S. nor the Canadian
fleets have ever caught the entire TAC.
The 10-year (2010–2019) average
utilization rate is 71.3 percent of the
coastwide TAC. The five-year average
utilization rate from 2010–2014 is
higher (78.1 percent) than the ten-year
average, while the 5-year average
utilization rate from 2015–2019 is lower
(64.5 percent). These averages provide a
realistic range for projecting the
utilization rates in 2020 and 2021.
The stock assessment indicates that
applying any of the estimated average
utilization rates to the range of
coastwide TACs we considered results
in relative spawning stock biomass
levels above B40 percent after one
fishing year (49–53 percent relative
spawning stock biomass). When
applying these coastwide TACs for 2
years, a TAC of 666,458 mt with the
higher utilization rates at 71 percent or
higher results in relative spawning stock
biomass levels below B40 percent (37
and 39 percent). Using the same
approach, a coastwide TAC of 597,500
mt and the highest utilization rate
(78.08 percent) would also result in the
relative spawning stock biomass level to
fall below B40 percent by the beginning
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of 2022. Although the Pacific whiting
TAC is set annually and could be
adjusted after the 2021 stock
assessment, the fact that these
projections result in spawning biomass
levels below B40 percent after 2 years
suggests that a TAC at the default
harvest level and last year’s TAC
(597,500 mt) may risk the sustainable
management of the Pacific whiting
resource.
Using the same approach as described
above, TACs of 575,000 mt and 555,000
mt combined with the highest
utilization rate being considered, result
in a projected harvest of 448,960 mt and
433,344 mt, respectively. The stock
assessment indicates that these levels of
harvest in 2020 would result in an
estimated relative spawning stock
biomass of 51 percent at the beginning
of 2021, which is well above the B40
percent level, and an estimated relative
spawning stock biomass of 40—41
percent at the beginning of 2022.
Overall, the stock assessment
indicates that the relative spawning
stock biomass of Pacific whiting has a
high probability of being lower at the
beginning of 2021 than 2020, ranging
from an 81 percent probability with no
harvest to a 97 percent probability at the
default harvest rate. Although a decline
is probable even in the absence of
fishing pressure, the decline is relatively
modest and does not threaten the
sustainability of the resource. At the
actual harvest rates under consideration
the stock assessment indicates there is
less than 33 percent chance of relative
spawning stock biomass falling below
B40 percent in 1 year, a less than 10
percent probability of falling below B25
percent, and essentially no chance of
falling below B10 percent after 1 year.
Continuing these harvest levels into a
second year does have an increased
chance of relative spawning stock
biomass falling below B40 percent. Two
years of actual harvests above
approximately 460,000 mt result in a
greater than 50 percent probability of
falling below B40 percent, a 20 percent
probability of falling below B25 percent,
and a 4 percent probability of falling
below B10 percent. The best scientific
information available indicates that
reduction from last year’s coastwide
TAC (597,500 mt), and deviation from
the Act’s default harvest rate, would
support the long-term sustainability of
the stock.
Economic Impacts of Potential Pacific
Whiting TAC Levels
The Pacific whiting fishery is the
highest volume fishery on the West
Coast of the United States, providing
hundreds of jobs. In 2019, total revenue
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was estimated to be $29 million in the
non-tribal shoreside sector and $35
million in the at-sea whiting sector. The
total non-tribal ex-vessel revenue in
2019 is estimated to have been about
$64 million. This is higher than the
2015–2019 inflation-adjusted average of
approximately $54 million. Maintaining
access to the Pacific whiting resource is
important for both direct fishery
participants and West Coast fishing
communities.
The starting and ending proposals
from Canada, 300,000 mt and 390,000
mt, represent a 49 percent and 35
percent reduction from the 2019 TAC,
respectively. Reductions of this
magnitude would have negative
economic impact on U.S. coastal
communities. Canada’s proposed TACs
reflect their concern with the declining
Pacific whiting biomass as the 2010 year
class ages, as well as uncertainty of the
recent recruitment strength since the
stock assessment is not able to predict
cohort strength until they are detected
by the acoustic survey and fishery.
However, the stock assessment indicates
that the higher TACs proposed by the
U.S. continue to provide a sustainable
Pacific whiting resource and result in
the relative spawning stock biomass
levels above B40 percent after 1 year,
and at or above B40 percent after 2 years
of fishing. Because of these factors,
NMFS has preliminarily determined
that a large reduction is not appropriate
but supports a measured reduction from
last year’s TAC.
2020 Pacific Whiting Adjusted TAC
Recommendation
The Act requires NMFS to make the
necessary adjustments to the TAC
specified in the Agreement (Paragraph 5
of Article II). The Agreement (Paragraph
5 of Article II) requires adjustments to
the coastwide TAC to account for
overages if either U.S. or Canadian catch
in the previous year exceeded its
individual TAC, or carryovers, if U.S. or
Canadian catch was less than its
individual TAC in the previous year.
Both the U.S. and Canada harvested less
than their individual TACs in 2019, and
therefore carryover is applied to the
2020 individual TACs.
Taking into account the percentage
shares for each country (26.12 percent
for Canada and 73.88 percent for the
U.S.) and the adjustments for uncaught
fish, as required by the Act, we
recommend a final adjusted coastwide
TAC of 575,000 mt, with a final adjusted
TAC for Canada of 150,190 mt (129,822
mt + 20,367 mt carryover adjustment),
and a final adjusted TAC for the US of
424,810 mt (367,202 mt + 57,608 mt
carryover adjustment). This
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recommendation is consistent with the
best available scientific information,
provisions of the Agreement, and the
Whiting Act.
Tribal Allocations
The regulations at 50 CFR 660.50(d)
identify the procedures for
implementing the treaty rights that
Pacific Coast treaty Indian tribes have to
harvest groundfish in their usual and
accustomed fishing areas in U.S. waters.
Tribes with treaty fishing rights in the
area covered by the Pacific Coast
Groundfish FMP request allocations,
set-asides, or regulations specific to the
tribes during the Council’s biennial
harvest specifications and management
measures process. The regulations state
that the Secretary will develop tribal
allocations and regulations in
consultation with the affected tribe(s)
and, insofar as possible, with tribal
consensus.
NMFS allocates a portion of the U.S.
TAC of Pacific whiting to the tribal
fishery, following the process
established in 50 CFR 660.50(d). The
tribal allocation is subtracted from the
U.S. Pacific whiting TAC before
allocation to the non-tribal sectors.
Four Washington coastal treaty Indian
tribes including the Makah Indian Tribe,
Quileute Indian Tribe, Quinault Indian
Nation, and the Hoh Indian Tribe
(collectively, the ‘‘Treaty Tribes’’), can
participate in the tribal Pacific whiting
fishery. Tribal allocations of Pacific
whiting have been based on discussions
with the Treaty Tribes regarding their
intent for those fishing years. The Hoh
Tribe has not expressed an interest in
participating in the Pacific whiting
fishery to date. The Quileute Tribe and
Quinault Indian Nation have expressed
interest in beginning to participate in
the Pacific whiting fishery at a future
date. To date, only the Makah Tribe has
prosecuted a tribal fishery for Pacific
whiting, and has harvested Pacific
whiting since 1996 using midwater
trawl gear. Table 1 below provides a
recent history of U.S. TACs and annual
tribal allocation in mt.
TABLE 1—U.S. TOTAL ALLOWABLE
CATCH AND ANNUAL TRIBAL ALLOCATION IN METRIC TONS
Year
2010
2011
2012
2013
2014
2015
2016
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..........
..........
..........
..........
..........
..........
..........
17APP1
U.S. TAC 1
(mt)
193,935
290,903
186,037
269,745
316,206
325,072
367,553
Tribal
Allocation
(mt)
49,939
66,908
48,556
63,205
55,336
56,888
64,322
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Council recommends the amount of
Pacific whiting to accommodate
incidental mortality of Pacific whiting
in research activities and nongroundfish fisheries based on estimates
of scientific research catch and
Tribal
U.S. TAC 1
estimated bycatch mortality in nonYear
Allocation
(mt)
(mt)
groundfish fisheries. At its November
2019 meeting, the Council
2017 ..........
441,433
77,251 recommended an incidental mortality
2018 ..........
441,433
77,251 set-aside of 1,500 mt for 2020. This is
2019 ..........
441,433
77,251
consistent with the amount set-aside for
1 Beginning in 2012, the United States startresearch and incidental mortality each
ed using the term Total Allowable Catch, or year since 2014. This rule proposes the
TAC, based on the Agreement between the Council’s recommendations.
Government of the United States of America
and the Government of Canada on Pacific Non-Tribal Harvest Guidelines and
Hake/Whiting. Prior to 2012, the terms Optimal
Allocations
Yield (OY) and ACL were used.
In addition to the tribal allocation,
In 2009, NMFS, the states of
this proposed rule establishes the
Washington and Oregon, and the Treaty
fishery harvest guideline (HG), called
Tribes started a process to determine the
the non-tribal allocation. The proposed
long-term tribal allocation for Pacific
2020 fishery HG for Pacific whiting is
whiting. However, these groups have
348,968 mt. This amount was
not yet determined a long-term
determined by deducting the 74,342 mt
allocation. In order to ensure Treaty
tribal allocation and the 1,500 mt
Tribes continue to receive allocations,
allocation for scientific research catch
this rule proposes the 2020 tribal
and fishing mortality in non-groundfish
allocation of Pacific whiting. This
fisheries from the total U.S. TAC of
allocation is not intended to set
424,810 mt. The Council recommends
precedent for future allocations.
the research and bycatch set-aside on an
In exchanges between NMFS and the
annual basis, based on estimates of
Treaty Tribes during November and
scientific research catch and estimated
December 2019, the Makah Tribe
bycatch mortality in non-groundfish
indicated their intent to participate in
fisheries. The regulations further
the tribal Pacific whiting fishery in 2020 allocate the fishery HG among the three
and requested 17.5 percent of the U.S.
non-tribal sectors of the Pacific whiting
TAC. The Quinault Indian Nation and
fishery: The catcher/processor (C/P)
Quileute Indian Tribe both informed
Coop Program, the Mothership (MS)
NMFS in December 2019 that they will
Coop Program, and the Shorebased
not participate in the 2020 fishery. The
Individual Fishing Quota (IFQ) Program.
Hoh Indian Tribe has, in previous years, The C/P Coop Program is allocated 34
indicated in conversations with NMFS
percent (118,649 mt for 2020), the MS
that they have no plans to fish for
Coop Program is allocated 24 percent
whiting in the foreseeable future and
(83,752 mt for 2020), and the
will contact NMFS if that changes.
Shorebased IFQ Program is allocated 42
NMFS will contact the Tribes during the percent (146,567 mt for 2020). The
proposed rule comment period to refine fishery south of 42° N lat. may not take
the 2020 allocation before allocating the more than 7,328 mt (5 percent of the
final U.S. TAC between the tribal and
Shorebased IFQ Program allocation)
non-tribal whiting fisheries. NMFS
prior to May 15, the start of the primary
proposes a tribal allocation that
Pacific whiting season north of 42° N
accommodates the Makah Tribe’s
lat.
request of 17.5 percent of the U.S. TAC.
The environmental assessment for the
The proposed 2020 U.S.TAC is 424,810
2019–2020 harvest specifications rule
(see Electronic Access) analyzed a range
mt, and therefore the proposed 2020
tribal allocation is 74,342 mt. NMFS has of TAC alternatives for 2020, and the
final 2020 TAC falls within this
determined that the current scientific
analyzed range. In addition, via the
information regarding the distribution
2019–2020 harvest specifications
and abundance of the coastal Pacific
whiting stock indicates the 17.5 percent rulemaking process, the public had an
opportunity to comment on the 2019–
is within the range of the tribal treaty
2020 TACs for whiting, just as they did
right to Pacific whiting.
for all species in the groundfish FMP.
Non-Tribal Research and Bycatch SetNMFS follows this process because,
Asides
unlike for all other groundfish species,
The U.S. non-tribal whiting fishery is
the TAC for whiting is decided in a
managed under the Council’s Pacific
highly abbreviated annual process from
Coast Groundfish FMP. Each year, the
February through April of every year,
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TABLE 1—U.S. TOTAL ALLOWABLE
CATCH AND ANNUAL TRIBAL ALLOCATION IN METRIC TONS—Continued
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and the normal rulemaking process
would not allow for the fishery to open
with the new TAC on the annual season
opening date of May 15.
TABLE 2—2020 PROPOSED PACIFIC
WHITING ALLOCATIONS IN METRIC
TONS
Sector
Tribal .....................................
Catcher/Processor (C/P)
Coop Program ...................
Mothership (MS) Coop Program ..................................
Shorebased IFQ Program ....
2020 Pacific
whiting
allocation
(mt)
74,342
118,649
83,752
146,567
2020 Harvest Specifications for Pacific
Coast Shortbelly Rockfish and Cowcod
South of 40≥10′ N Latitude
Shortbelly rockfish and cowcod south
of 40°10′ N latitude are managed under
the Pacific Coast Groundfish FMP. The
FMP requires that the Council set
harvest specifications and management
measures for groundfish at least
biennially. NMFS established 2019 and
2020 harvest specifications including
overfishing limits (OFLs), allowable
biological catches (ABCs), ACLs and
management measures such as annual
catch targets (ACTs) for groundfish
stocks in December 2018 (83 FR 63970,
December 12, 2018). In June 2019, the
Council and NMFS received public
comment from affected stakeholders
that low catch limits for two stocks,
cowcod south of 40°10′ N latitude and
shortbelly rockfish, were preventing
vessels from harvesting co-occurring
healthy fish stocks because of increased
bycatch levels. The Council held
meetings in September and November
2019 to identify a range of alternatives
for each stock and select final preferred
alternatives to recommend for
implementation. This proposed rule is
based on the Council’s final
recommendations made at its November
2019 meeting. The Council deemed the
proposed regulations consistent with
and necessary to implement the
proposed actions in a March 19, 2020
letter. The Analysis identifies the
preferred alternatives and other decision
points and is posted on the NMFS West
Coast Region web page (see ADDRESSES)
along with this proposed rule.
The Council and NMFS consider the
proposed actions consistent with
provisions in the Pacific Coast
Groundfish FMP, which allows changes
to the harvest specifications and
adjustments to management measures
on a schedule other than the typical
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biennial cycle under special
circumstances.
Shortbelly Rockfish (Sebastes jordani)
This rule proposes to implement the
Council recommendation from its
November 2019 meeting, to increase the
2020 ACL for shortbelly rockfish to
3,000 mt. The remaining shortbelly
rockfish catch limits for 2020, including
the OFL and ABC, are unchanged from
those implemented in the 2019–2020
Pacific Coast Groundfish Biennial
Harvest Specifications (83 FR 63970,
December 12, 2018). The proposed
changes are summarized in Table 3
below.
TABLE 3—COMPARISON OF NO ACTION ALTERNATIVE AND PROPOSED 2020 HARVEST SPECIFICATIONS AND MANAGEMENT
MEASURES FOR SHORTBELLY ROCKFISH IN METRIC TONS
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OFL ..........................................................................................................................................................................
ABC ..........................................................................................................................................................................
ACL ..........................................................................................................................................................................
Fishery Harvest Guideline .......................................................................................................................................
Shortbelly rockfish (Sebastes jordani)
is one of the most abundant rockfish
species and an important forage species
in the California Current Ecosystem.
Unlike most harvested Pacific coast
rockfishes (e.g., bocaccio and cowcod),
shortbelly rockfish are small-bodied,
relatively short-lived and semi-pelagic
rockfish that school as adults.
Shortbelly rockfish recruitment is
highly variable among years, causing
populations to undergo large ‘‘booms
and busts’’.
Historically, shortbelly rockfish was
most abundant off central California
from Monterey Bay to Point Reyes,
common in southern California, and
only rarely encountered north of Cape
Mendocino, California. In recent years,
shortbelly rockfish distribution has
extended north of Cape Mendocino,
California and into Oregon and
Washington waters, the principal
fishing areas the midwater trawl fishery
operates in to harvest Pacific whiting.
While shortbelly rockfish bycatch was
historically low in the Pacific whiting
fishery, the recent shift in distribution
and a likely increase in abundance, is
resulting in increased bycatch of
shortbelly rockfish in the Pacific
whiting midwater trawl fishery.
Shortbelly rockfish was last assessed
in 2007. The assessment, available on
the Council’s website at https://
www.pcouncil.org/documents/2007/04/
stock-assessment-model-for-theshortbelly-rockfish-sebastes-jordani-inthe-california-current.pdf/, estimated
the shortbelly rockfish stock to be 67
percent of unfished levels at the start of
2005. Given that the population size is
known to be highly dynamic, it is
possible that the population size and
distribution changed in the recent years.
The Analysis describes NMFS survey
data, including the Southwest Fisheries
Science Center’s Rockfish Recruitment
and Ecosystem Analysis Survey
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(RREAS) and California Cooperative
Oceanic Fisheries Investigations
(CalCOFI) and the Northwest Fisheries
Science Center’s West Coast Groundfish
Bottom Trawl Survey. The data show
extraordinarily high recruitment events
occurred between 2013 and 2017, and
provide evidence that the overall
shortbelly rockfish population was very
high in 2018–2019. The population size
in southern California remains close to
average levels and suggests shortbelly
rockfish population did not simply shift
to northern waters. Increased
encounters of shortbelly rockfish in
northern midwater trawl fisheries is
likely the result of increased
recruitment and coastwide biomass
coupled with an expansion of its
geographic range on the West Coast.
In addition to examining NMFS
survey data for trends in shortbelly
rockfish biomass and distribution, the
Analysis describes that forage species
other than shortbelly rockfish
(specifically northern anchovy) were
unusually abundant, and that there was
higher than average production of
several marine predators in 2018–19.
Shortbelly rockfish is not targeted by
west coast fisheries. Given its
importance as a forage species, the
Council considered classifying
shortbelly rockfish as an ecosystem
component species in the 2013–14
biennial management cycle following
the revision of National Standard 1
guidelines. The Council decided to
retain shortbelly rockfish as a stock
actively managed in the fishery in the
Pacific Coast Groundfish FMP, which
requires that the Council set an OFL,
ABC, and ACL for this stock as part of
the biennial harvest specifications
process. The shortbelly rockfish default
harvest control rule is used to set the
ACL each biennial cycle. The current
default harvest control rule is a constant
catch value intended to accommodate
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6,950
5,789
500
483
6,950
5,789
3,000
2,983
observed bycatch levels, discourage
targeting, and continue to protect the
availability of shortbelly rockfish as a
forage species. The Council
recommended a low ACL of 50 mt in
2011–2012 Pacific Coast Groundfish
Biennial Harvest Specifications and
Management Measures (76 FR 27508,
May 11, 2011) to discourage
development of any targeted fishery,
and accommodate incidental bycatch of
shortbelly rockfish, while allowing the
remaining harvestable surplus of the
stock to be available as forage fish in the
ecosystem. The ACL was increased from
50 to 500 mt in the 2015–2016 Pacific
Coast Groundfish Biennial Harvest
Specifications and Management
Measures (80 FR 12567, March 10, 2015)
to accommodate a potential increase in
bycatch as a midwater rockfish fishery
re-emerged following the rebuilding of
widow rockfish.
Shortbelly rockfish catch remained
low and well below the ACL of 500 mt
until 2017 when it increased from 30 mt
to 320 mt. The Analysis describes
annual catch of shortbelly rockfish.
High bycatch of shortbelly rockfish in
the whiting sectors resulted in the
fishery exceeding the ACLs in 2018 (508
mt) and 2019 (approximately 655 mt).
In the absence of this proposed rule
to increase the 2020 shortbelly rockfish
ACL, a future shortbelly rockfish
overage could result in early closure of
the Pacific whiting and non-whiting
midwater trawl fisheries, which could
have negative economic consequences
for vessels, processors, and
communities. The magnitude of
economic losses due to early fishery
closure from attaining the shortbelly
rockfish ACL is difficult to project and
is dependent on which fisheries would
close and when they would close. The
Analysis describes impacts of potential
closures of the midwater trawl fisheries
targeting whiting and pelagic rockfish
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that are most likely to incur a large
bycatch of shortbelly rockfish and be
subject to an early closure if the
shortbelly rockfish ACL is attained. The
range of predicted impacts in terms of
foregone income is $4.6 million to
$175.2 million depending on whether
there is a late season closure in
December or an earlier closure in June.
This action proposes changes to the
shortbelly ACL are consistent with
Section 5.5.1 of the Pacific Coast
Groundfish FMP, which states:
‘‘. . .OFLs, ABCs, ACLs, OYs, ACTs,
HGs, and quotas may only be modified
in cases where a harvest specification
announced at the beginning of the
biennial fishing period is found to have
resulted from incorrect data or from
computational errors. If the Council
finds that such an error has occurred, it
may recommend the Secretary publish a
notice in the Federal Register revising
the incorrect harvest specification at the
earliest possible date.’’
The 2018 West Coast Groundfish
Observer Program data and estimates of
shortbelly rockfish bycatch were not
available when setting the 2019 and
2020 harvest specifications and this new
information compels this consideration.
Increasing the shortbelly rockfish ACL
to 3,000 mt for the final half of the 2020
fishing year would accommodate
incidental bycatch of the shortbelly
rockfish stock given recent high bycatch
in groundfish trawl fisheries, while
continuing to minimize bycatch,
discourage development of a targeted
fishery for shortbelly rockfish, and
continuing to protect the availability of
shortbelly rockfish as important forage
in the California Current Ecosystem.
The increase of the 2020 ACL is not
anticipated to induce targeting of
shortbelly. Industry has indicated that
shortbelly rockfish is not currently
marketable and does not expect it to
become so in the near future. The low
ex-vessel price of $0.01-$0.03 per pound
in recent years supports industry reports
that the fish is primarily used as
fishmeal or discarded at-sea. The
median West Coast limited entry trawl
permitted vessel has variable operating
costs of $0.46 per pound, according to
the most recent Economic Data
Collection Report, and is unlikely to
pursue a targeting strategy for such a
low value species, as the revenues
would be less than typical operating
costs. Industry also provided testimony
that they avoid catching shortbelly
rockfish because the spines of shortbelly
rockfish degrade Pacific whiting quality
as they are impinged in the codend.
The proposed rule continues to
protect the availability of shortbelly
rockfish as important forage in the
California Current Ecosystem. Scientific
information currently available provides
evidence of above average forage
conditions in the California Current
Ecosystem with higher abundances of
forage species such as anchovy and a
high overall shortbelly rockfish
population in 2018–2019. Further, the
higher ACL under the proposed rule is
well below the shortbelly rockfish OFL
of 6,950 mt, and ABC of 5,789 mt.
The proposed rule is an
accountability measure that addresses
the operational issue of a low ACL that
resulted in ACL overages in 2018 and
2019. National Standard 1 Guidelines
state: ’’On an annual basis, the Council
must determine as soon as possible after
21377
the fishing year if an ACL was exceeded.
If an ACL was exceeded, AMs must be
implemented as soon as possible to
correct the operational issue that caused
the ACL overage, as well as any
biological consequences to the stock or
stock complex resulting from the
overage when it is known.’’
The proposed increase would
improve the performance and
effectiveness of the ACL by increasing
the ACL to better correspond with
recent trends in shortbelly rockfish
abundance and bycatch rates in the
groundfish fishery. This would reduce
the risk of an ACL overage in 2020,
which would potentially close midwater
trawl fisheries and cause adverse
economic impacts to West Coast fishing
communities while continuing to
protect the availability of shortbelly
rockfish as important forage in the
California Current Ecosystem.
Cowcod (Sebastes levis) South of 40°10′
N Latitude
This proposed rule would remove the
cowcod ACT of 6 mt and reduce the
research catch set-aside to 1 mt for
cowcod south of 40°10′ N. latitude in
2020. The ACL would remain at 10 mt.
The 2020 cowcod annual vessel limit
would increase from 858 pounds (.4 mt)
to 1,264 pounds (.6 mt) for affected
participants in the limited entry trawl
fishery south of 40°10′ N. latitude. The
proposed changes are summarized in
Table 4 below. This action would
reduce the risk that vessels in the trawl
IFQ program reach their annual vessel
limit for cowcod in 2020 and have to
cease fishing in the trawl IFQ program
for the remainder of the year.
TABLE 4—SUMMARY OF THE FEATURES OF THE NO ACTION AND PREFERRED ALTERNATIVES FOR COWCOD SOUTH OF
40°10′ N LATITUDE IN METRIC TONS, EXCEPT WHERE NOTED AS POUNDS
jbell on DSKJLSW7X2PROD with PROPOSALS
OFL .........................................................................................................................................................
ABC .........................................................................................................................................................
ACL .........................................................................................................................................................
Research Set-aside ................................................................................................................................
Fishery HG ..............................................................................................................................................
ACT .........................................................................................................................................................
Non-Trawl Allocation (64 percent of the ACL) .......................................................................................
Trawl Allocation (36 percent of the ACL) ...............................................................................................
Annual Vessel Limit (17.7 percent of trawl allocation) ...........................................................................
Increase in vessel limit ...........................................................................................................................
Increase in vessel limit (percent) ............................................................................................................
Updated information on cowcod
research conducted by the Northwest
Fisheries Science Center and other
entities indicates that a lower set-aside
will accommodate planned research
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activities without a risk of exceeding the
ACL.
Cowcod south of 40°10′ N latitude
was declared overfished in January
2000. In 2001, NMFS closed most of
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76 ...........................
68 ...........................
10 ...........................
2 .............................
8 .............................
6 .............................
3.8 ..........................
2.2 ..........................
0.4 (858 pounds) ...
0 .............................
0 .............................
76
68
10
1
9
Removed
5.8
3.2
0.6 (1,264 pounds)
0.2 (406 pounds)
47
their habitat in the Southern California
Bight (SCB) south of Point Conception
at 34°27′ N latitude to bottom fishing.
The Council adopted and NMFS
implemented a rebuilding plan for the
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stock under Amendment 16–3 to the
Pacific Coast Groundfish FMP (69 FR
57874, September 28, 2004), revised the
rebuilding plan for the stock under
Amendment 16–4 in 2007 (71 FR 78638,
December 29, 2006) and again under
Amendment 16–5 in 2011 (76 FR 77415,
December 13, 2011). Using the
spawning potential ratio harvest control
rate of 82.7 percent specified in the
most recent rebuilding plan, the median
time to rebuild was estimated to be 2068
at that time.
Harvest specifications and
management measures for cowcod in
the 2019–20 biennial management
period were based on the 2013
rebuilding analysis and consistent with
the rebuilding plan provisions. Cowcod
stock assessments and rebuilding
analyses are available on the Council’s
website at https://www.pcouncil.org/
stock-assessments-star-reports-statreports-rebuilding-analyses-terms-ofreference/groundfish-stock-assessmentdocuments/. The 2013 assessment and
rebuilding analysis concluded that the
cowcod stock is rebuilding much more
quickly than anticipated under its
rebuilding plan.
The 2020 cowcod harvest
specifications and management
measures were established as part of the
2019–2020 Pacific Coast Groundfish
Biennial Harvest Specifications and
Management Measures (83 FR 63970,
December 12, 2018). The Stock
Assessment and Fishery Evaluation
(SAFE) document posted on the
Council’s website at https://
www.pcouncil.org/documents/2019/01/
status-of-the-pacific-coast-groundfishfishery-stock-assessment-and-fisheryevaluation-description-of-the-fisheryrevised-january-2019.pdf/ contains a
detailed description of cowcod, its
status and management, as well as the
Council’s Scientific and Statistical
Committee’s approach for rebuilding
analyses.
The Southwest Fisheries Science
Center completed a new stock
assessment for cowcod in 2019 and the
spawning stock depletion at the start of
2019 is at 57 percent of unfished levels,
which is above the 40 percent target.
The 2019 stock assessment is available
on the Council’s website at https://
www.pcouncil.org/documents/2019/10/
status-of-cowcod-sebastes-levis-in-2019october-24-2019.pdf/. NMFS declared
the stock rebuilt effective September 30,
2019 in the 2019 Quarter 3 Status of the
Stocks report available at https://
www.fisheries.noaa.gov/national/
population-assessments/fishery-stockstatus-updates. As a result of the
cowcod rebuilding, the Council and
NMFS will consider changes to cowcod
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catch limits in establishing the 2021–
2022 Pacific Coast Groundfish Biennial
Harvest Specifications and Management
Measures. This proposed rule does not
consider a change to the 2020 rebuilding
harvest control rule. The ACL would
remain at 10 mt.
To keep mortality of the stocks
managed under the Pacific Coast
Groundfish FMP within the ACLs, the
Council also recommends management
measures. Pacific Coast Groundfish FMP
Section 6.2D describes the process for
modifying management measures,
which includes a two Council meeting
process and a regulatory amendment.
Management measures are intended to
rebuild overfished stocks, prevent catch
from exceeding the ACLs, and allow for
the harvest of healthy stocks. The 2019–
2020 Pacific Coast Groundfish Biennial
Harvest Specifications and Management
Measures established an ACT of 6 mt for
both 2019 and 2020 to address the
uncertainty in research impacts and
ensure total mortality is within the ACL.
The ACT functions as a fishery harvest
guideline and is the amount allocated
across groundfish trawl and non-trawl
fisheries. The current specifications
allocated 2 mt of cowcod for research.
Updated information on cowcod
research is now available and indicates
that a lower set-aside of 1 mt would
accommodate planned research
activities. Over the past several years,
cowcod harvest has consistently been
far below the ACL and ACT.
The Pacific Coast Groundfish Trawl
Catch Share Program (75 FR 60868,
October 1, 2010 and 75 FR 78343,
December 15, 2010) issued IFQ to
limited entry trawl participants. In
addition to IFQ, the program established
annual vessel limits for IFQ species to
prevent any one entity from having
excessive control of a stock during a
fishing year. The 2020 cowcod annual
vessel limit of 858 pounds (389.182 kg)
is based on an apportionment (17.7
percent) of the trawl allocation of the 6
mt ACT (Table 3).
The low overall catch limits of
cowcod have prevented the Shorebased
IFQ bottom trawlers from accessing
healthy co-occurring groundfish stocks
and in some years have resulted in
vessels ending their fishing season
early. Although the cowcod stock is
now rebuilt, the timing of the biennial
groundfish specification cycle means
that the fleet would not benefit from less
restrictive cowcod catch limits until
2021. This proposed action would
reduce the risk that vessels fishing south
of 40°10′ N lat. in the groundfish trawl
IFQ program would reach their annual
vessel limit for cowcod in 2020 and
have to cease fishing in the trawl IFQ
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program for the remainder of the year,
which would result in severe adverse
economic impacts for those vessels and
the fishing communities reliant on the
trawl fishery south of 40°10′ N lat.
This proposed rule would be
implemented under the statutory and
regulatory authority of section 304(b)
and 305(d) of the Magnuson-Stevens
Act, and the Pacific Whiting Act of
2006. With this proposed rule, NMFS,
acting on behalf of the Secretary, would
ensure that the FMP is implemented in
a manner consistent with treaty rights of
four Treaty Tribes to fish in their ‘‘usual
and accustomed grounds and stations’’
in common with non-tribal citizens.
United States v. Washington, 384 F.
Supp. 313 (W.D. Wash. 1974).
III. Classification
NMFS notes that the public comment
period for this proposed rule is 15 days.
As a result of the requirements to amend
reallocation provisions and announce
Pacific whiting harvest guidelines by
the Pacific whiting season start date,
May 15th, NMFS has determined that a
15-day comment period best balances
the interest in allowing the public
adequate time to comment on the
proposed measures while implementing
the management measures and
announcing the Pacific whiting
allocations.
Pursuant to section 304 (b)(1)(A) and
305 (d) of the Magnuson-Stevens Act,
the NMFS Assistant Administrator has
determined that this proposed rule is
consistent with the Pacific Coast
Groundfish FMP, other provisions of the
Magnuson-Stevens Act, and other
applicable law, subject to further
consideration after public comment. In
making its final determination, NMFS
will take into account the complete
record, including the data, views, and
comments received during the comment
period.
Pursuant to Executive Order 13175,
this proposed rule was developed after
meaningful consultation and
collaboration with tribal officials from
the area covered by the Pacific Coast
Groundfish FMP. Under the MagnusonStevens Act at 16 U.S.C. 1852(b)(5), one
of the voting members of the Pacific
Council must be a representative of an
Indian tribe with federally recognized
fishing rights from the area of the
Council’s jurisdiction. In addition,
regulations implementing the Pacific
Coast Groundfish FMP establish a
procedure by which the tribes with
treaty fishing rights in the area covered
by the Pacific Coast Groundfish FMP
request new allocations or regulations
specific to the tribes, in writing, before
the first of the two meetings at which
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the Council considers groundfish
management measures. The regulations
at 50 CFR 660.324(d) further state, ‘‘the
Secretary will develop tribal allocations
and regulations under this paragraph in
consultation with the affected tribe(s)
and, insofar as possible, with tribal
consensus.’’ The tribal management
measures in this proposed rule have
been developed following these
procedures.
The Office of Management and Budget
has determined that this proposed rule
is not significant for purposes of
Executive Order 12866. This proposed
rule is not an Executive Order 13771
regulatory action because this rule is not
significant under Executive Order
12866.
The Council and NMFS prepared an
Integrated Analysis for the shortbelly
rockfish and cowcod actions, which
address the statutory requirements of
the Magnuson-Stevens Act, the National
Environmental Policy Act, Presidential
Executive Order 12866, and the
Regulatory Flexibility Act. As part of
this Analysis, an environmental
assessment (EA) was prepared that
describes the impact on the human
environment that would result from
implementation of the proposed
shortbelly rockfish action. The full suite
of alternatives analyzed by the Council
can be found on the Council’s website
at www.pcouncil.org. This Analysis does
not contain all the alternatives because
a range of potential total harvest levels
for Pacific whiting and cowcod, which
these actions would simply allocate
among user groups, have been
considered under the Final
Environmental Impact Statement for
Harvest Specifications and Management
Measures for 2015–2016 and Biennial
Periods thereafter (2015/16 FEIS) and in
the Environmental Assessment for
Harvest Specifications and Management
Measures for 2019–2020 and Biennial
Periods Thereafter and is available from
NMFS (see ADDRESSES). The 2015/16
FEIS examined the harvest
specifications and management
measures for 2015–16 and 10 year
projections for routinely adjusted
harvest specifications and management
measures. The 10 year projections were
produced to evaluate the impacts of the
ongoing implementation of harvest
specifications and management
measures and to evaluate the impacts of
the routine adjustments that are the
main component of each biennial cycle.
Therefore, the EA for the 2019–20 cycle
tiers from the 2015/16 FEIS and focuses
on the harvest specifications and
management measures that were not
within the scope of the 10 year
projections in the 2015/16 FEIS. A copy
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of the EA for shortbelly rockfish, which
is included as part of the Analysis, is
available from NMFS (see ADDRESSES).
This action also announces a public
comment period on the EA for
shortbelly rockfish.
Initial Regulatory Flexibility Analyses
(IRFA) were prepared for this action, as
required by section 603 of the
Regulatory Flexibility Act (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,
and the legal basis for this action is
contained in the SUMMARY section and at
the beginning of the SUPPLEMENTARY
INFORMATION section of the preamble. A
summary of the IRFA follow. Copies of
the IRFAs are available from NMFS (See
ADDRESSES).
Under the RFA, the term ‘‘small
entities’’ includes small businesses,
small organizations, and small
governmental jurisdictions. The Small
Business Administration has established
size criteria for entities involved in the
fishing industry that qualify as small
businesses. A business involved in fish
harvesting is a small business if it is
independently owned and operated and
not dominant in its field of operation
(including its affiliates) and if it has
combined annual receipts, not in excess
of $11 million for all its affiliated
operations worldwide (see 80 FR 81194,
December 29, 2015). A wholesale
business servicing the fishing industry
is a small business if it employs 100 or
fewer persons on a full time, part time,
temporary, or other basis, at all its
affiliated operations worldwide. A
seafood processor is a small business if
it is independently owned and operated,
not dominant in its field of operation,
and employs 750 or fewer persons on a
full time, part time, temporary, or other
basis, at all its affiliated operations
worldwide. For purposes of rulemaking,
NMFS is also applying the seafood
processor standard to catcher processors
because Pacific whiting CatcherProcessors (C/Ps) earn the majority of
the revenue from processed seafood
product.
Description and Estimate of the Number
of Small Entities to Which the Rule
Applies, and Estimate of Economic
Impacts by Entity Size and Industry
This proposed rule would affect how
Pacific whiting is allocated to the
following sectors/programs: Tribal,
Shorebased IFQ Program Trawl Fishery,
MS Coop Program Whiting At-sea Trawl
Fishery, and C/P Coop Program Whiting
At-sea Trawl Fishery. The amount of
Pacific whiting allocated to these sectors
is based on the U.S. TAC. We expect
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21379
one tribal entity to fish for Pacific
whiting in 2020. Tribes are not
considered small entities for the
purposes of RFA. Impacts to tribes are
nevertheless considered in this analysis.
As of January 2020, the Shorebased IFQ
Program is composed of 167 Quota
Share permits/accounts (134 of which
were allocated whiting quota pounds),
and 41 first receivers, two of which are
designated as whiting-only receivers
and 15 that may receive both whiting
and non-whiting. These regulations also
directly affect participants in the MS
Co-op Program, a general term to
describe the limited access program that
applies to eligible harvesters and
processors in the MS sector of the
Pacific whiting at-sea trawl fishery. This
program currently consists of six MS
processor permits, and a catcher vessel
fleet currently composed of a single coop, with 34 Mothership/Catcher Vessel
(MS/CV) endorsed permits (with three
permits each having two catch history
assignments). These regulations also
directly affect the C/P Co-op Program,
composed of 10 C/P endorsed permits
owned by three companies that have
formed a single coop. These co-ops are
considered large entities from several
perspectives; they have participants that
are large entities, and have in total more
than 750 employees worldwide
including affiliates. Although there are
three non-tribal sectors, many
companies participate in two sectors
and some participate in all three sectors.
As part of the permit application
processes for the non-tribal fisheries,
based on a review of the Small Business
Administration size criteria, permit
applicants are asked if they considered
themselves a ‘‘small’’ business, and they
are asked to provide detailed ownership
information. Data on employment
worldwide, including affiliates, are not
available for these companies, which
generally operate in Alaska as well as
the West Coast and may have operations
in other countries as well. NMFS has
limited entry permit holders self-report
size status. For 2020, all 10 CP permits
reported they are not small businesses,
as did 8 mothership catcher vessels.
There is substantial, but not complete
overlap between permit ownership and
vessel ownership so there may be a
small number of additional small entity
vessel owners who will be impacted by
this rule. After accounting for cross
participation, multiple QS account
holders, and affiliation through
ownership, NMFS estimates that there
are 106 non-tribal entities directly
affected by these proposed regulations,
85 of which are considered ‘‘small’’
businesses.
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This rule will allocate Pacific whiting
between tribal and non-tribal harvesters
(a mixture of small and large
businesses). Tribal fisheries consist of a
mixture of fishing activities that are
similar to the activities that non-tribal
fisheries undertake. Tribal harvests may
be delivered to both shoreside plants
and motherships for processing. These
processing facilities also process fish
harvested by non-tribal fisheries. The
effect of the tribal allocation on nontribal fisheries will depend on the level
of tribal harvests relative to their
allocation and the reapportionment
process. If the tribes do not harvest their
entire allocation, there are opportunities
during the year to reapportion
unharvested tribal amounts to the nontribal fleets. For example, in 2019 NMFS
reapportioned 40,000 mt of the original
77,251 mt tribal allocation. This
reapportionment was based on
conversations with the tribes and the
best information available at the time,
which indicated that this amount would
not limit tribal harvest opportunities for
the remainder of the year. The
reapportioning process allows
unharvested tribal allocations of Pacific
whiting to be fished by the non-tribal
fleets, benefitting both large and small
entities. The revised Pacific whiting
allocations for 2019 following the
reapportionment were: Tribal 37,251 mt,
C/P Co-op 136,912 mt; MS Co-op 96,644
mt; and Shorebased IFQ Program
169,126 mt.
The prices for Pacific whiting are
largely determined by the world market
because most of the Pacific whiting
harvested in the U.S. is exported. The
U.S. Pacific whiting TAC is highly
variable, as have subsequent harvests
and ex-vessel revenues. For the years
2015 to 2019, the total Pacific whiting
fishery (tribal and non-tribal) averaged
harvests of approximately 281,205 mt
annually. The 2019 U.S. non-tribal
fishery had a catch of approximately
312,500 mt, and the tribal fishery
landed approximately 4,000 mt.
Impacts to Makah catcher vessels who
elect to participate in the tribal fishery
are measured with an estimate of exvessel revenue. In lieu of more complete
information on tribal deliveries, total exvessel revenue is estimated with the
2019 average shoreside ex-vessel price
of Pacific whiting, which was $200 per
mt. At that price, the proposed 2020
tribal allocation of 74,342 mt would
have an ex-vessel value of $14.9 million.
Shortbelly Rockfish
The proposed rule would primarily
affect limited entry trawl vessels,
especially midwater trawl vessels
targeting Pacific whiting and semi-
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pelagic rockfish (i.e., non-whiting) north
of 40°10′ N latitude given the sectors
and gear experiencing the highest
bycatch of shortbelly rockfish in recent
years. The entities fishing for Pacific
whiting (described in detail above), and
the 14–20 vessels fishing in the nonwhiting midwater trawl fishery in 2017–
2018, would be affected. The preferred
shortbelly rockfish alternative would
have neutral to positive impacts for
limited entry trawl participants fishing
in the Pacific whiting and non-whiting
midwater fisheries.
Cowcod South of 40°10′ N Latitude
The proposed rule would directly
impact two groups: Quota share owners
of cowcod south of 40°10′ N latitude
and catcher vessel owners who operate
vessels south of 40°10′ N latitude and
have the potential to encounter cowcod.
There are 62 entities that own 2020
cowcod quota and 7 vessels that caught
cowcod south of 40°10′ N. latitude in
2019 that would be impacted by this
rule. The preferred cowcod alternative
would have neutral to positive impacts
for limited entry trawl participants who
own quota for this species and/or fish
south of 40°10′ N latitude. Quota
owners that are able to sell increased
quota amounts may benefit. Most IFQ
vessels do not operate south of 40°10′ N
latitude and would experience no
impacts from the preferred alternative.
A Description of any Significant
Alternatives to the Proposed Rule That
Accomplish the Stated Objectives of
Applicable Statutes and That Minimize
any Significant Economic Impact of the
Proposed Rule on Small Entities
NMFS considered two alternatives for
the Pacific whiting action: The ‘‘No
Action’’ and the ‘‘Proposed Action.’’
NMFS considered a range of alternatives
for the Pacific whiting coastwide TAC.
A coastwide TAC of 555,000 mt has
greater economic impacts for 2020 than
what is proposed is this rule (a
coastwide TAC of 575,000 mt). Higher
coastwide TACs considered in the range
(597,500 mt and 666,480 mt) would
have less economic impact for 2020.
However, 2020 assessment projections
indicate these higher catch levels may
result in near-term stock biomass
declines below target levels. This is
contrary to the Whiting Act and
Agreement, which requires sustainable
management of the Pacific whiting
resource.
NMFS did not consider a broader
range of alternatives to the proposed
tribal allocation. The tribal allocation is
based primarily on the requests of the
tribes. These requests reflect the level of
participation in the fishery that will
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allow them to exercise their treaty right
to fish for Pacific whiting. Under the
Proposed Action alternative, NMFS
proposes to set the tribal allocation
percentage at 17.5 percent, as requested
by the Tribes. This would yield a tribal
allocation of 74,342 mt for 2020.
Consideration of a percentage lower
than the tribal request of 17.5 percent is
not appropriate in this instance. As a
matter of policy, NMFS has historically
supported the harvest levels requested
by the Tribes. Based on the information
available to NMFS, the tribal request is
within their tribal treaty rights. A higher
percentage would arguably also be
within the scope of the treaty right.
However, a higher percentage would
unnecessarily limit the non-tribal
fishery.
Under the no action alternative,
NMFS would not set a coastwide TAC
or make an allocation to the tribal
sector. This alternative was considered,
but the Act requires the U.S. to establish
TACs to sustainably manage the Pacific
whiting resource. The regulatory
framework provides for a tribal
allocation on an annual basis only.
Therefore, the no action alternative
would result in no allocation of Pacific
whiting to the tribal sector in 2020,
which would be inconsistent with
NMFS’ responsibility to manage the
fishery consistent with the tribes’ treaty
rights. Given that there is a tribal
request for allocation in 2020, this
alternative received no further
consideration.
Shortbelly Rockfish
The Council and NMFS considered
three alternatives for shortbelly rockfish:
No action, specifying a 2020 ACL of
3,000 mt and specifying a 2020 ACL of
4,184 mt. Under the no action
alternative, NMFS would not change the
2020 ACL for shortbelly rockfish. This
no action alternative has the highest risk
of an early fishery closure and lost
revenue for Pacific whiting and LE nonwhiting midwater trawl fisheries and
communities. The range of predicted
impacts in terms of foregone income is
$4.6 million to $175.2 million
depending on whether there is a late
season closure in December or an earlier
closure in June.
The proposed measure for shortbelly
rockfish would reduce the risk of an
early closure for midwater trawl
fisheries due to the possibility of high
bycatch of shortbelly rockfish in 2020,
and avoid the adverse economic impacts
to West Coast fishing communities that
would result from such closures or
constraints. The proposed measure to
establish the 2020 ACL at 3,000 mt
rather than the alternative of 4,184 mt,
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should be sufficient to avoid
constraining the midwater trawl fishery
while continuing to ensure more than
adequate shortbelly rockfish as forage.
Cowcod
The Council and NMFS considered no
action and alternatives to provide relief
on limited entry trawl participants
fishing south of 40°10′ N latitude,
including removing the ACT and
adjustments to the research set-aside
amounts. Under the no action
alternative, NMFS would not change the
ACT or research set-aside amounts. This
no action alternative would result in
potential loss of revenue if vessels reach
their cowcod individual vessel limit and
are required to cease fishing for the
remainder of the year.
The proposed measure for cowcod
would eliminate the 2020 ACT of 6 mt
for cowcod south of 40°10′ N latitude
and reduce the research set-aside
amount to 1 mt. The annual vessel limit
for cowcod would increase from 858 lbs
(.4 mt) to 1,264 lbs (.6 mt). This
alternative meets the stated purpose and
need to reduce the risk that IFQ vessels
south of 40°10′ N latitude will reach
their individual vessel limits of cowcod
in 2020 and have to cease fishing in the
IFQ fishery for the remainder of the
year, which would result in adverse
economic impacts on those vessels and
fishing communities in the area. The
Council considered an alternative to
remove the ACT of 6 mt and reduce the
research set-aside to 0.5 mt. This
alternative may have resulted in a lesser
economic impact on vessels and fishing
communities, but it did not provide an
adequate amount of cowcod for
research.
Regulatory Flexibility Act (RFA)
Determination of No Significant Impact
NMFS determined this proposed rule
would not adversely affect small
entities. The reapportioning process
allows unharvested tribal allocations of
Pacific whiting, fished by small entities,
to be fished by the non-tribal fleets,
benefitting both large and small entities.
The shortbelly and cowcod measures
will assist small entities by reducing the
risk of early closures due to bycatch.
The shortbelly rockfish and cowcod
measures are temporary and will be in
effect for less than 1 year.
NMFS has prepared IRFAs and is
requesting comments on this
conclusion. See ADDRESSES.
There are no reporting, recordkeeping
or other compliance requirements in the
proposed rule.
No Federal rules have been identified
that duplicate, overlap, or conflict with
this action.
List of Subjects in 50 CFR Part 660
Fisheries, Fishing, Indian Fisheries.
Dated: April 13, 2020.
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 660 is proposed
to be 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 § 660.50, revise paragraph (f)(4)
to read as follows:
■
§ 660.50 Pacific Coast treaty Indian
fisheries.
*
*
*
*
*
(f) * * *
(4) Pacific whiting. The tribal
allocation for 2020 will be 74,342 mt.
*
*
*
*
*
■ 3. Revise table 2a to part 660, subpart
C, to read as follows:
TABLE 2a TO PART 660, SUBPART C—2020, AND BEYOND, SPECIFICATION OF OFL, ABC, ACL, ACT AND FISHERY
HARVEST GUIDELINES
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[Weights in metric tons]
Stocks/stock complexes
Area
OFL
ABC
ACL a
Fishery HG b
COWCOD c .........................................................
COWCOD ...........................................................
COWCOD ...........................................................
YELLOWEYE ROCKFISH d ...............................
Arrowtooth Flounder e .........................................
Big Skate f ...........................................................
Black Rockfish g ..................................................
Black Rockfish h ..................................................
Bocaccio i ............................................................
Cabezon j ............................................................
California Scorpionfish k .....................................
Canary Rockfish l ................................................
Chilipepper Rockfish m .......................................
Darkblotched Rockfish n .....................................
Dover Sole° ........................................................
English Sole p .....................................................
Lingcod q .............................................................
Lingcod r .............................................................
Longnose Skate s ...............................................
Longspine Thornyhead t .....................................
Longspine Thornyhead u ....................................
Pacific Cod v .......................................................
Pacific Whiting w .................................................
Pacific Ocean Perch x .........................................
Petrale Sole y ......................................................
Sablefish z ...........................................................
Sablefish aa .........................................................
Shortbelly Rockfish bb .........................................
Shortspine Thornyhead cc ...................................
Shortspine Thornyhead dd ..................................
S of 40°10′ N lat ...............................................
(Conception) .....................................................
(Monterey) .........................................................
Coastwide .........................................................
Coastwide .........................................................
Coastwide .........................................................
California (S of 42° N lat.) ................................
Washington (N of 46°16′ N lat.) .......................
S of 40°10′ N lat ...............................................
California (S of 42° N lat.) ................................
S of 34°27′ N lat ...............................................
Coastwide .........................................................
S of 40°10′ N lat ...............................................
Coastwide .........................................................
Coastwide .........................................................
Coastwide .........................................................
N of 40°10′ N lat ...............................................
S of 40°10′ N lat ...............................................
Coastwide .........................................................
N of 34°27′ N lat ...............................................
S of 34°27′ N lat ...............................................
Coastwide .........................................................
Coastwide .........................................................
N of 40°10′ N lat ...............................................
Coastwide .........................................................
N of 36° N lat ....................................................
S of 36° N lat ....................................................
Coastwide .........................................................
N of 34°27′ N lat ...............................................
S of 34°27′ N lat ...............................................
76
62
13
84
15,306
541
341
311
2,104
153
331
1,431
2,521
853
92,048
11,101
4,768
977
2,474
3,901
..............
3,200
666,458
4,632
2,976
8,648
..............
6,950
3,063
..............
68
57
11
77
12,750
494
326
297
2,011
146
307
1,368
2,410
815
87,998
10,135
4,558
934
2,365
3,250
............
2,221
( w)
4,229
2,845
7,896
............
5,789
2,551
............
10
NA
NA
49
12,750
494
326
297
2,011
146
307
1,368
2,410
815
50,000
10,135
4,541
869
2,000
2,470
780
1,600
( w)
4,229
2,845
5,723
2,032
3,000
1,669
883
9
NA
NA
43
10,655
452
325
279
1,965
146
305
1,301
2,325
781
48,404
9,919
4,263
858
1,852
2,420
779
1,094
348,968
4,207
2,524
See Table 2c
2,028
2,983
1,604
882
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TABLE 2a TO PART 660, SUBPART C—2020, AND BEYOND, SPECIFICATION OF OFL, ABC, ACL, ACT AND FISHERY
HARVEST GUIDELINES—Continued
[Weights in metric tons]
Stocks/stock complexes
Area
OFL
Spiny Dogfish ee .................................................
Splitnose Rockfish ff ............................................
Starry Flounder gg ...............................................
Widow Rockfish hh ..............................................
Yellowtail Rockfish ii ............................................
Black Rockfish/Blue Rockfish/Deacon Rockfish jj
Cabezon/Kelp Greenling kk .................................
Cabezon/Kelp Greenling ll ..................................
Nearshore Rockfish mm .......................................
Shelf Rockfish nn .................................................
Slope Rockfish oo ................................................
Nearshore Rockfish pp ........................................
Shelf Rockfish qq .................................................
Slope Rockfish rr .................................................
Other Flatfish ss ..................................................
Other Fish tt ........................................................
Coastwide .........................................................
S of 40°10′ N lat ...............................................
Coastwide .........................................................
Coastwide .........................................................
N of 40°10′ N lat ...............................................
Oregon (Between 46°16′ N lat. and 42° N lat.)
Oregon (Between 46°16′ N lat. and 42° N lat.)
Washington (N of 46°16′ N lat.) .......................
N of 40°10′ N lat ...............................................
N of 40°10′ N lat ...............................................
N of 40°10′ N lat ...............................................
S of 40°10′ N lat ...............................................
S of 40°10′ N lat ...............................................
S of 40°10′ N lat ...............................................
Coastwide .........................................................
Coastwide .........................................................
2,472
1,810
652
11,714
6,261
670
216
12
92
2,302
1,873
1,322
1,919
855
8,202
286
ABC
ACL a
2,059
1,731
452
11,199
5,986
611
204
10
82
2,048
1,732
1,165
1,626
743
6,041
239
2,059
1,731
452
11,199
5,986
611
204
10
82
2,048
1,732
1,163
1,625
743
6,041
239
a Annual
1,726
1,714
433
10,951
4,941
609
204
10
79
1,971
1,651
1,159
1,546
723
5,792
230
catch limits (ACLs), annual catch targets (ACTs) and harvest guidelines (HGs) are specified as total catch values.
HGs means the HG or quota after subtracting Pacific Coast treaty Indian tribes allocations and projected catch, projected research
catch, deductions for fishing mortality in non-groundfish fisheries, and deductions for EFPs from the ACL or ACT.
c Cowcod south of 40°10′ N lat. 1 mt is deducted from the ACL to accommodate EFP fishing (less than 0.1 mt) and research activity, resulting
in a fishery HG of 9 mt. Any additional mortality in research activities will be deducted from the ACL.
d Yelloweye rockfish. The 49 mt ACL is based on the current rebuilding plan with a target year to rebuild of 2029 and an SPR harvest rate of
65 percent. 6.1 mt is deducted from the ACL to accommodate the Tribal fishery (2.3 mt), the incidental open access fishery (0.62 mt), EFP catch
(0.24 mt) and research catch (2.92 mt), resulting in a fishery HG of 43 mt. The non-trawl HG is 39.5 mt. The non-nearshore HG is 2.1 mt and the
nearshore HG is 6.2 mt. Recreational HGs are: 10.2 mt (Washington); 9.1 mt (Oregon); and 11.9 mt (California). In addition, there are the following ACTs: Non-nearshore (1.7 mt), nearshore (4.9 mt), Washington recreational (8.1 mt), Oregon recreational (7.2 mt), and California recreational (9.4 mt).
e Arrowtooth flounder. 2,094.9 mt is deducted from the ACL to accommodate the Tribal fishery (2,041 mt), the incidental open access fishery
(40.8 mt), EFP fishing (0.1 mt), and research catch (13 mt), resulting in a fishery HG of 10,655 mt.
f Big skate. 41.9 mt is deducted from the ACL to accommodate the Tribal fishery (15 mt), the incidental open access fishery (21.3 mt), EFP
fishing (0.1 mt), and research catch (5.5 mt), resulting in a fishery HG of 452 mt.
g Black rockfish (California). 1.3 mt is deducted from the ACL to accommodate EFP fishing (1.0 mt) and the incidental open access fishery (0.3
mt), resulting in a fishery HG of 325 mt.
h Black rockfish (Washington). 18.1 mt is deducted from the ACL to accommodate the Tribal fishery (18 mt) and research catch (0.1 mt), resulting in a fishery HG of 279 mt.
i Bocaccio south of 40°10′ N lat. The stock is managed with stock-specific harvest specifications south of 40°10′ N lat. and within the Minor
Shelf Rockfish complex north of 40°10′ N lat. 46.1 mt is deducted from the ACL to accommodate the incidental open access fishery (0.5 mt),
EFP catch (40 mt) and research catch (5.6 mt), resulting in a fishery HG of 1,965 mt. The California recreational fishery has an HG of 827.2 mt.
j Cabezon (California). 0.3 mt is deducted from the ACL to accommodate the incidental open access fishery, resulting in a fishery HG of 146
mt.
k California scorpionfish south of 34°27′ N lat. 2.4 mt is deducted from the ACL to accommodate the incidental open access fishery (2.2 mt)
and research catch (0.2 mt), resulting in a fishery HG of 305 mt.
l Canary rockfish. 67.1 mt is deducted from the ACL to accommodate the Tribal fishery (50 mt), the incidental open access fishery (1.3 mt),
EFP catch (8 mt), and research catch (7.8 mt), resulting in a fishery HG of 1,301 mt. Recreational HGs are: 44.3 mt (Washington); 66.5 mt (Oregon); and 119.7 mt (California).
m Chilipepper rockfish south of 40°10′ N lat. Chilipepper are managed with stock-specific harvest specifications south of 40°10′N lat. and within
the Minor Shelf Rockfish complex north of 40°10′ N lat. 84.9 mt is deducted from the ACL to accommodate the incidental open access fishery
(11.5 mt), EFP fishing (60 mt), and research catch (13.4 mt), resulting in a fishery HG of 2,325 mt.
n Darkblotched rockfish. 33.8 mt is deducted from the ACL to accommodate the Tribal fishery (0.2 mt), the incidental open access fishery (24.5
mt), EFP catch (0.6 mt), and research catch (8.5 mt) resulting in a fishery HG of 781 mt.
oDover sole. 1,595.6 mt is deducted from the ACL to accommodate the Tribal fishery (1,497 mt), the incidental open access fishery (49.3 mt),
EFP fishing (0.1 mt), and research catch (49.2 mt), resulting in a fishery HG of 48,404 mt.
p English sole. 216.2 mt is deducted from the ACL to accommodate the Tribal fishery (200 mt), the incidental open access fishery (8.1 mt),
EFP fishing (0.1 mt), and research catch (8 mt), resulting in a fishery HG of 9,919 mt.
q Lingcod north of 40°10′ N lat. 278 mt is deducted from the ACL for the Tribal fishery (250 mt), the incidental open access fishery (9.8 mt),
EFP catch (1.6 mt) and research catch (16.6 mt), resulting in a fishery HG of 4,263 mt.
r Lingcod south of 40°10′ N lat. 11.3 mt is deducted from the ACL to accommodate the incidental open access fishery (8.1 mt) and research
catch (3.2 mt), resulting in a fishery HG of 858 mt.
s Longnose skate. 148.3 mt is deducted from the ACL to accommodate the Tribal fishery (130 mt), incidental open access fishery (5.7 mt),
EFP catch (0.1 mt), and research catch (12.5 mt), resulting in a fishery HG of 1,852 mt.
t Longspine thornyhead. 50.4 mt is deducted from the ACL to accommodate the Tribal fishery (30 mt), the incidental open access fishery (6.2
mt), and research catch (14.2 mt), resulting in a fishery HG of 2,420 mt.
u Longspine thornyhead south of 34°27′ N lat. 1.4 mt is deducted from the ACL to research catch, resulting in a fishery HG of 779 mt.
v Pacific cod. 506.2 mt is deducted from the ACL to accommodate the Tribal fishery (500 mt), EFP catch (0.1 mt), research catch (5.5 mt), and
the incidental open access fishery (0.6 mt), resulting in a fishery HG of 1,094 mt.
w Pacific whiting. The 2020 OFL of 666,458 mt is based on the 2020 assessment with an F40% of FMSY proxy. The proposed 2020 coastwide
adjusted Total Allowable Catch (TAC) is 575,000 mt. The U.S. TAC is 73.88 percent of the coastwide TAC. The proposed 2020 adjusted U.S.
TAC is 424,810 mt (367,202 mt unadjusted TAC + 57,608 mt carryover adjustment). From the adjusted U.S. TAC, 74,342 mt is deducted to accommodate the Tribal fishery, and 1,500 mt is deducted to accommodate research and bycatch in other fisheries, resulting in a 2020 fishery HG
of 348,968 mt. The TAC for Pacific whiting is established under the provisions of the Agreement with Canada on Pacific Hake/Whiting and the
Pacific Whiting Act of 2006, 16 U.S.C. 7001–7010, and the international exception applies. Therefore, no ABC or ACL values are provided for
Pacific whiting.
x Pacific ocean perch north of 40°10′ N lat. 22.4 mt is deducted from the ACL to accommodate the Tribal fishery (9.2 mt), the incidental open
access fishery (10 mt), EFP fishing (0.1 mt), and research catch (3.1 mt)-resulting in a fishery HG of 4,207 mt.
b Fishery
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y Petrale sole. 320.6 mt is deducted from the ACL to accommodate the Tribal fishery (290 mt), the incidental open access fishery (6.4 mt), EFP
catch (0.1 mt), and research catch (24.1 mt), resulting in a fishery HG of 2,524 mt.
z Sablefish north of 36° N lat. The 40–10 adjustment is applied to the ABC to derive a coastwide ACL value because the stock is in the precautionary zone. This coastwide ACL value is not specified in regulations. The coastwide ACL value is apportioned north and south of 36° N lat.,
using the 2003–2014 average estimated swept area biomass from the NMFS NWFSC trawl survey, with 73.8 percent apportioned north of 36° N
lat. and 26.2 percent apportioned south of 36° N lat. The northern ACL is 5,723 mt and is reduced by 572 mt for the Tribal allocation (10 perceN
of the ACL north of 36° N lat.). The 572 mt Tribal allocation is reduced by 1.5 percent to account for discard mortality. Detailed sablefish allocations are shown in Table 2c.
aa Sablefish south of 36° N lat. The ACL for the area south of 36° N lat. is 2,032 mt (26.2 percent of the calculated coastwide ACL value). 4.2
mt is deducted from the ACL to accommodate the incidental open access fishery (1.8 mt) and research catch (2.4 mt), resulting in a fishery HG
of 2,028 mt.
bb Shortbelly rockfish. 17.2 mt is deducted from the ACL to accommodate the incidental open access fishery (8.9 mt), EFP catch (0.1 mt), and
research catch (8.2 mt), resulting in a fishery HG of 2,983 mt.
cc Shortspine thornyhead north of 34°27′ N lat. 65.3 mt is deducted from the ACL to accommodate the Tribal fishery (50 mt), the incidental
open access fishery (4.7 mt), EFP catch (0.1 mt), and research catch (10.5 mt), resulting in a fishery HG of 1,604 mt for the area north of 34°27′
N lat.
dd Shortspine thornyhead south of 34°27′ N lat. 1.2 mt is deducted from the ACL to accommodate the incidental open access fishery (0.5 mt)
and research catch (0.7 mt), resulting in a fishery HG of 882 mt for the area south of 34°27′ N lat.
ee Spiny dogfish. 333 mt is deducted from the ACL to accommodate the Tribal fishery (275 mt), the incidental open access fishery (22.6 mt),
EFP catch (1.1 mt), and research catch (34.3 mt), resulting in a fishery HG of 1,726 mt.
ff Splitnose rockfish south of 40°10′ N lat. Splitnose rockfish in the north is managed in the Slope Rockfish complex and with stock-specific harvest specifications south of 40°10′ N lat. 16.6 mt is deducted from the ACL to accommodate the incidental open access fishery (5.8 mt), research
catch (9.3 mt) and EFP catch (1.5 mt), resulting in a fishery HG of 1,714 mt.
gg Starry flounder. 18.8 mt is deducted from the ACL to accommodate the Tribal fishery (2 mt), EFP catch (0.1 mt), research catch (0.6 mt),
and the incidental open access fishery (16.1 mt), resulting in a fishery HG of 433 mt.
hh Widow rockfish. 248.4 mt is deducted from the ACL to accommodate the Tribal fishery (200 mt), the incidental open access fishery (3.1 mt),
EFP catch (28 mt) and research catch (17.3 mt), resulting in a fishery HG of 10,951 mt.
ii Yellowtail rockfish north of 40°10′ N lat. 1,045.1 mt is deducted from the ACL to accommodate the Tribal fishery (1,000 mt), the incidental
open access fishery (4.5 mt), EFP catch (20 mt) and research catch (20.6 mt), resulting in a fishery HG of 4,941 mt.
jj Black rockfishBlue rockfishDeacon rockfish (Oregon). 1.2 mt is deducted from the ACL to accommodate the incidental open access fishery
(0.3 mt) and EFP catch (0.9 mt), resulting in a fishery HG of 609 mt.
kk CabezonKelp greenling (Oregon). 0.2 mt is deducted from the ACL to accommodate EFP catch, resulting in a fishery HG of 204 mt.
ll CabezonKelp greenling (Washington). There are no deductions from the ACL so the fishery HG is equal to the ACL of 10 mt.
mm Nearshore Rockfish north of 40°10′ N lat. 2.8 mt is deducted from the ACL to accommodate the Tribal fishery (1.5 mt), EFP catch (0.1 mt),
research catch (0.3), and the incidental open access fishery (0.9 mt), resulting in a fishery HG of 79 mt.
nn Shelf Rockfish north of 40°10′ N lat. 76.9 mt is deducted from the ACL to accommodate the Tribal fishery (30 mt), the incidental open access fishery (17.7 mt), EFP catch (4.5 mt), and research catch (24.7 mt), resulting in a fishery HG of 1,971 mt.
oo Slope Rockfish north of 40°10′ N lat. 80.8 mt is deducted from the ACL to accommodate the Tribal fishery (36 mt), the incidental open access fishery (21.7 mt), EFP catch (1.5 mt), and research catch (21.6 mt), resulting in a fishery HG of 1,651 mt.
pp Nearshore Rockfish south of 40°10′ N lat. 4.1 mt is deducted from the ACL to accommodate the incidental open access fishery (1.4 mt) and
research catch (2.7 mt), resulting in a fishery HG of 1,159 mt.
qq Shelf Rockfish south of 40°10′ N lat. 79.1 mt is deducted from the ACL to accommodate the incidental open access fishery (4.6 mt), EFP
catch (60 mt), and research catch (14.5 mt), resulting in a fishery HG of 1,546 mt.
rr Slope Rockfish south of 40°10′ N lat. 20.2 mt is deducted from the ACL to accommodate the incidental open access fishery (16.9 mt), EFP
catch (1 mt), and research catch (2.3 mt), resulting in a fishery HG of 723 mt. Blackgill rockfish has a stock-specific HG for the entire groundfish
fishery south of 40°10′ N lat. set equal to the species’ contribution to the 40–10-adjusted ACL. Harvest of blackgill rockfish in all groundfish fisheries south of 40°10′ N lat. counts against this HG of 159 mt.
ss Other Flatfish. The Other Flatfish complex is comprised of flatfish species managed in the PCGFMP that are not managed with stock-specific OFLs/ABCs/ACLs. MoS of the species in the Other Flatfish complex are unassessed and include: butter sole, curlfin sole, flathead sole, Pacific sanddab, rock sole, sand sole, and rex sole. 249.5 mt is deducted from the ACL to accommodate the Tribal fishery (60 mt), the incidental
open access fishery (161.6 mt), EFP fishing (0.1 mt), and research catch (27.8 mt), resulting in a fishery HG of 5,792 mt.
tt Other Fish. The Other Fish complex is comprised of kelp greenling off California and leopard shark coastwide. 8.9 mt is deducted from the
ACL to accommodate the incidental open access fishery (8.8 mt) and research catch (0.1 mt), resulting in a fishery HG of 230 mt.
4. Revise table 2b to part 660, subpart
C, to read as follows:
■
TABLE 2b TO PART 660, SUBPART C—2020, AND BEYOND, ALLOCATIONS BY SPECIES OR SPECIES GROUP
[Weight in metric tons]
jbell on DSKJLSW7X2PROD with PROPOSALS
Stocks/stock complexes
Arrowtooth flounder .............
Big skate a ...........................
Bocaccio a ...........................
Canary rockfish a b ...............
Chilipepper rockfish ............
COWCOD a .........................
Darkblotched rockfish c .......
Dover sole ...........................
English sole .........................
Lingcod ................................
Lingcod ................................
Longnose skate a ................
Longspine thornyhead ........
Pacific cod ...........................
Pacific whiting d ...................
Pacific ocean perch e ..........
VerDate Sep<11>2014
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Fishery HG or
ACT a b
Area
Coastwide ...........................
Coastwide ...........................
S of 40°10′ N lat .................
Coastwide ...........................
S of 40°10′ N lat .................
S of 40°10′ N lat .................
Coastwide ...........................
Coastwide ...........................
Coastwide ...........................
N of 40′10° N lat ................
S of 40′10° N lat .................
Coastwide ...........................
N of 34°27′ N lat ................
Coastwide ...........................
Coastwide ...........................
N of 40°10′ N lat ................
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10,655.1
452.1
1,964.9
1,300.9
2,325.1
9.0
781.2
48,404.4
9,918.8
4,263.0
857.7
1,851.7
2,419.6
1,093.8
348,968
4,206.6
Fmt 4702
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Trawl
%
Non-trawl
Mt
95
95
39
72
75
36
95
95
95
45
45
90
95
95
100
95
%
10,122.3
429.5
767.1
940.3
1,743.8
3.2
742.1
45,984.2
9,422.9
1,918.4
386.0
1,666.5
2,298.6
1,039.1
348,968
3,996.3
E:\FR\FM\17APP1.SGM
17APP1
Mt
5
5
61
28
25
64
5
5
5
55
55
10
5
5
0
5
532.8
22.6
1,197.8
360.6
581.3
5.8
39.1
2,420.2
495.9
2,344.7
471.7
185.2
121.0
54.7
0
210.3
21384
Federal Register / Vol. 85, No. 75 / Friday, April 17, 2020 / Proposed Rules
TABLE 2b TO PART 660, SUBPART C—2020, AND BEYOND, ALLOCATIONS BY SPECIES OR SPECIES GROUP—Continued
[Weight in metric tons]
Stocks/stock complexes
Trawl
Fishery HG or
ACT a b
Area
Petrale sole .........................
Coastwide ...........................
2,524.4
Sablefish .............................
N of 36° N lat .....................
NA
Sablefish .............................
Shortspine thornyhead ........
Shortspine thornyhead ........
Splitnose rockfish ................
Starry flounder ....................
Widow rockfish f ..................
YELLOWEYE ROCKFISH ..
Yellowtail rockfish ...............
Minor Shelf Rockfish North
Minor Shelf Rockfish South
Minor Slope Rockfish North
Minor Slope Rockfish South
Other Flatfish ......................
S of 36° N lat .....................
N of 34°27′ N lat ................
S of 34°27′ N lat .................
S of 40°10′ N lat .................
Coastwide ...........................
Coastwide ...........................
Coastwide ...........................
N of 40°10′ N lat ................
N of 40°10′ N lat ................
S of 40°10′ N lat .................
N of 40°10′ N lat ................
S of 40°10′ N lat .................
Coastwide ...........................
2,027.8
1,603.7
881.8
1,714.4
433.2
10,950.6
42.9
4,940.9
1,971.1
1,545.9
1,651.2
722.8
5,791.5
%
Non-trawl
Mt
95
%
2,398.2
Mt
5
126.2
58
5
NA
5
50
9
92
12
39.8
87.8
19
37
10
1,176.1
80.2
831.8
85.7
216.6
985.6
39.5
592.9
784.5
1,357.3
313.7
267.4
579.2
See Table 2c
42
95
NA
95
50
91
8
88
60.2
12.2
81
63
90
851.7
1,523.5
50.0
1,628.7
216.6
9,965.0
3.4
4,348.0
1,186.6
188.6
1,337.5
455.4
5,212.4
a
Allocations decided through the biennial specification process.
mt of the total trawl allocation of canary rockfish is allocated to the MS and C/P sectors, as follows: 30 mt for the MS sector, and 16 mt for
the C/P sector.
c Consistent with regulations at § 660.55(c), 9 percent (66.8 mt) of the total trawl allocation for darkblotched rockfish is allocated to the Pacific
whiting fishery, as follows: 28.1 mt for the Shorebased IFQ Program, 16.0 mt for the MS sector, and 22.7 mt for the C/P sector. The tonnage calculated here for the Pacific whiting IFQ fishery contributes to the total shorebased trawl allocation, which is found at § 660.140(d)(1)(ii)(D).
d Consistent with regulations at § 660.55(i)(2), the commercial harvest guideline for Pacific whiting is allocated as follows: 34 percent (118,649
mt) for the C/P Coop Program; 24 percent (83,752 mt) for the MS Coop Program; and 42 percent (146,567 mt) for the Shorebased IFQ Program.
No more than 5 percent of the Shorebased IFQ Program allocation (7,328 mt) may be taken and retained south of 42° N lat. before the start of
the primary Pacific whiting season north of 42° N lat.
e Consistent with regulations at § 660.55(c), 17 percent (679.4 mt) of the total trawl allocation for Pacific ocean perch is allocated to the Pacific
whiting fishery, as follows: 285.3 mt for the Shorebased IFQ Program, 163.0 mt for the MS sector, and 231.0 mt for the C/P sector. The tonnage
calculated here for the Pacific whiting IFQ fishery contributes to the total shorebased trawl allocation, which is found at § 660.140(d)(1)(ii)(D).
f Consistent with regulations at § 660.55(c), 10 percent (996.5 mt) of the total trawl allocation for widow rockfish is allocated to the whiting fisheries, as follows: 418.5 mt for the shorebased IFQ fishery, 239.2 mt for the mothership fishery, and 338.8 mt for the catcher/processor fishery.
The tonnage calculated here for the whiting portion of the shorebased IFQ fishery contributes to the total shorebased trawl allocation, which is
found at § 660.140(d)(1)(ii)(D).
b 46
5. In § 660.140, revise paragraph
(d)(1)(ii)(D) to read as follows:
■
§ 660.140
*
*
Shorebased IFQ Program.
*
*
*
(d) * * *
(1) * * *
(ii) * * *
(D) Pacific whiting and non-whiting
QP shorebased trawl allocations. For the
trawl fishery, NMFS will issue QP based
on the following shorebased trawl
allocations:
jbell on DSKJLSW7X2PROD with PROPOSALS
TABLE 1 TO PARAGRAPH (d)(1)(II)(D)
IFQ species
Area
Arrowtooth flounder ......................................................
Bocaccio .......................................................................
Canary rockfish .............................................................
Chilipepper ....................................................................
COWCOD .....................................................................
Darkblotched rockfish ...................................................
Dover sole ....................................................................
English sole ..................................................................
Lingcod .........................................................................
Lingcod .........................................................................
Longspine thornyhead ..................................................
Minor Shelf Rockfish complex ......................................
Minor Shelf Rockfish complex ......................................
Minor Slope Rockfish complex .....................................
Minor Slope Rockfish complex .....................................
Other Flatfish complex .................................................
Pacific cod ....................................................................
Pacific ocean perch ......................................................
Pacific whiting ...............................................................
Petrale sole ...................................................................
Sablefish .......................................................................
Coastwide .....................................................................
South of 40°10′ N lat ....................................................
Coastwide .....................................................................
South of 40°10′ N lat ....................................................
South of 40°10′ N lat ....................................................
Coastwide .....................................................................
Coastwide .....................................................................
Coastwide .....................................................................
North of 40°10′ N lat ....................................................
South of 40°10′ N lat ....................................................
North of 34°27′ N lat ....................................................
North of 40°10′ N lat ....................................................
South of 40°10′ N lat ....................................................
North of 40°10′ N lat ....................................................
South of 40°10′ N lat ....................................................
Coastwide .....................................................................
Coastwide .....................................................................
North of 40°10′ N lat ....................................................
Coastwide .....................................................................
Coastwide .....................................................................
North of 36° N lat .........................................................
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17APP1
2019
Shorebased
trawl allocation
(mt)
2020
Shorebased
trawl allocation
(mt)
12,735.1
800.7
953.6
1,838.3
2.2
658.4
45,979.2
9,375.1
2,051.9
462.5
2,420.0
1,155.2
188.6
1,248.8
456.0
5,603.7
1,034.1
3,697.3
152,326.5
2,453.0
2,581.3
10,052.3
767.1
894.3
1,743.8
3.2
703.4
45,979.2
9,417.9
1,903.4
386.0
2,293.6
1,151.6
188.6
1,237.5
455.4
5,192.4
1,034.1
3,602.2
146,567
2,393.2
2,636.8
Federal Register / Vol. 85, No. 75 / Friday, April 17, 2020 / Proposed Rules
21385
TABLE 1 TO PARAGRAPH (d)(1)(II)(D)—Continued
IFQ species
Area
Sablefish .......................................................................
Shortspine thornyhead .................................................
Shortspine thornyhead .................................................
Splitnose rockfish .........................................................
Starry flounder ..............................................................
Widow rockfish .............................................................
YELLOWEYE ROCKFISH ............................................
Yellowtail rockfish .........................................................
South of 36° N lat .........................................................
North of 34°27′ N lat ....................................................
South of 34°27′ N lat ....................................................
South of 40°10′ N lat ....................................................
Coastwide .....................................................................
Coastwide .....................................................................
Coastwide .....................................................................
North of 40°10′ N lat ....................................................
*
*
*
*
*
[FR Doc. 2020–08019 Filed 4–16–20; 8:45 am]
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BILLING CODE 3510–22–P
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17APP1
2019
Shorebased
trawl allocation
(mt)
2020
Shorebased
trawl allocation
(mt)
834.0
1,506.8
50.0
1,646.7
211.6
9,928.8
3.4
4,305.8
851.7
1,493.5
50.0
1,628.7
211.6
9,387.1
3.4
4,048.0
Agencies
[Federal Register Volume 85, Number 75 (Friday, April 17, 2020)]
[Proposed Rules]
[Pages 21372-21385]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2020-08019]
[[Page 21372]]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 660
[Docket No. 200410-0109]
RIN 0648-BJ53
Magnuson-Stevens Act Provisions; Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery; 2020 Harvest Specifications for
Pacific Whiting, Cowcod and Shortbelly Rockfish and 2020 Pacific
Whiting Tribal Allocation
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Proposed rule; request for comments.
-----------------------------------------------------------------------
SUMMARY: This proposed rule would establish 2020 harvest specifications
and management measures for Pacific whiting, shortbelly rockfish and
cowcod taken in the U.S. exclusive economic zone off the coasts of
Washington, Oregon and California consistent with the Magnuson-Stevens
Fishery Conservation and Management Act, the Pacific Whiting Act of
2006, and other applicable laws. This rule proposes 2020 harvest
specifications for Pacific whiting including the U.S. and coastwide
Total Allowable Catch (TAC), the 2020 tribal allocation for the Pacific
whiting fishery, allocations for three commercial whiting sectors, and
set-asides for Pacific whiting research and incidental mortality in
other fisheries. The proposed rule would also adjust the 2020 harvest
specifications for shortbelly rockfish and cowcod. The proposed
measures are intended to help prevent overfishing, achieve optimum
yield, and ensure that management measures are based on the best
scientific information available.
DATES: Comments on this proposed rule must be received no later than
May 4, 2020.
ADDRESSES: You may submit comments on this document, identified by
NOAA-NMFS-2020-0027 by any of the following methods:
Electronic Submission: Submit all electronic public
comments via the Federal eRulemaking Portal. Go to www.regulations.gov/#!docketDetail;D=NOAA-NMFS-2020-0027 click the ``Comment Now!'' icon,
complete the required fields, and enter or attach your comments.
Mail: Barry Thom, c/o Stacey Miller, Sustainable Fisheries
Division, West Coast Region, NMFS, 1201 NE Lloyd Blvd. Suite 1100,
Portland, OR 97232.
Instructions: Comments sent by any other method, to any other
address or individual, or received after the end of the comment period,
may not be considered by NMFS. All comments received are 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, address, etc.), 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).
Electronic Access
This proposed rule is accessible via the internet at the Office of
the Federal Register website at https://www.federalregister.gov.
Background information and documents including an integrated analysis
for this action (Analysis), which addresses the statutory requirements
of the Magnuson Stevens Fishery Conservation and Management Act
(Magnuson-Stevens Act), the National Environmental Policy Act,
Presidential Executive Order 12866, and the Regulatory Flexibility Act
are available at the NMFS website at https://www.fisheries.noaa.gov/action/2020-harvest-specifications-pacific-whiting-cowcod-and-shortbelly-rockfish-and-2020-pacific and at the Pacific Fishery
Management Council's website at https://www.pcouncil.org/.
FOR FURTHER INFORMATION CONTACT: Stacey Miller, phone: 503-231-6290,
and email: [email protected].
SUPPLEMENTARY INFORMATION:
Background
This proposed rule includes actions for the Pacific whiting tribal
and non-tribal fisheries, shortbelly rockfish and cowcod. These actions
are combined into one proposed rule because they all relate to
establishing catch limits and management measures for Pacific Coast
groundfish stocks in 2020. This rule proposes determining the 2020
Pacific whiting coastwide TAC, and establishing the Pacific whiting
U.S. TAC based on the coastwide TAC, tribal allocation, allocations for
three commercial whiting sectors, and set-asides for research and
incidental mortality of Pacific whiting as recommended by the Pacific
Fishery Management Council (Council); increasing the 2020 annual catch
limit (ACL) for shortbelly rockfish; and eliminating the 2020 annual
catch target (ACT) and reducing the research set-aside for cowcod. The
allocations for Pacific whiting would be effective until December 31,
2020. The adjusted catch limits for cowcod and shortbelly would
supersede those put in place for 2020 through the 2019-2020 Pacific
Coast Groundfish Biennial Harvest Specifications and Management
Measures (83 FR 63970, December 12, 2018), and are being analyzed as
part of the 2021-2022 Pacific Coast Groundfish Biennial Harvest
Specifications and Management Measures, which are anticipated to be
effective on January 1, 2021.
Pacific Whiting
Background on the Pacific Whiting Agreement
The transboundary stock of Pacific whiting is managed through the
Agreement Between the Government of the United States of America and
the Government of Canada on Pacific Hake/Whiting of 2003, Nov. 21,
2003, T.I.A.S. 08-625 (Agreement). The Agreement establishes bilateral
bodies to implement its terms, including: The Joint Management
Committee (JMC), which recommends the TAC for Pacific whiting; the
Joint Technical Committee (JTC), which conducts the Pacific whiting
stock assessment; the Scientific Review Group (SRG), which reviews the
stock assessment; and the Advisory Panel (AP), which provides
stakeholder input to the JMC.
The Agreement establishes a default harvest policy of F-40 percent,
which means a fishing mortality rate that would reduce the spawning
biomass, calculated on a per recruit basis, to 40 percent of what it
would have been in absence of fishing mortality. The U.S. and Canada
may choose a different fishing mortality rate if they determine that
scientific evidence demonstrates that a different rate is necessary to
sustain the offshore Pacific whiting resource. The Agreement also
explicitly allocates 73.88 percent of the Pacific whiting TAC to the
U.S. and 26.12 percent of the TAC to Canada.
Based on the advice from the Treaty's JTC, SRG, and AP, the Treaty
specifies that the JMC shall recommend to the parties an overall
Pacific whiting TAC by March 25th of each year. In years when the JMC
does make a TAC recommendation to the parties, NMFS (under the
delegation of authority from the Secretary of Commerce) approves the
U.S. TAC with concurrence from the Department of State. The U.S. TAC is
allocated into tribal and non-tribal sectors.
[[Page 21373]]
The 2020 JMC negotiations were held from March 11-13, 2020, via the
internet, but did not result in a bilateral agreement on the coastwide
TAC. Based on the most current information, the stock assessment
estimates a TAC of 666,458 metric tons (mt) based on the default
harvest policy. The final Canadian proposal was 390,000 mt and the
final U.S. proposal was 555,000 mt for the adjusted coastwide TAC. The
Agreement does not specify a procedure for when the JMC does not agree
on a coastwide TAC. However, the 2006 Pacific Whiting Act (16 U.S.C.
7006(c)) identifies procedures for when the JMC does not recommend a
final TAC. The Act states that NMFS (as delegated by the Secretary of
Commerce) should establish the Pacific whiting TAC, taking into account
recommendations from the JMC, JTC, SRG, AP, and Council. The Act
requires NMFS to base the TAC decision on the best scientific
information available, and use the default harvest rate unless
scientific information indicates a different rate is necessary to
sustain the Pacific whiting resource. The Act also requires NMFS to
establish the U.S. share of the TAC based on the U.S./Canada percentage
split and adjustments specified in the Agreement.
2020 Pacific Whiting Stock Assessment and Scientific Review
The JTC completed a stock assessment for Pacific whiting in
February 2020 (available at https://www.fisheries.noaa.gov/resource/document/2020-pacific-hake-whiting-stock-assessment). The assessment
presents a model that uses an acoustic survey biomass index, catches of
the transboundary Pacific whiting stock, and age compositions to
estimate the biomass of the current stock. The most recent survey,
conducted collaboratively between the Canadian Department of Fisheries
and Oceans and NMFS, was completed in 2019. Age-composition data from
the acoustics survey and fishery catch provide information to estimate
relative year class strength. Pacific whiting displays high recruitment
variability relative to other west coast groundfish stocks, and
typically an occasional large year-class supports much of the fishery.
The Pacific whiting stock is currently supported by multiple above
average cohorts simultaneously, including the 2010, 2014, 2016, and
2017 year classes, which is highly unusual. The current assessment
estimates the 2010 year class as the second highest recruitment in the
assessment time series. The 2014 and 2016 year classes are estimated to
be above average in strength and the 2017 year is about average,
however there is high uncertainty around the strength of these later
year classes. The assessment estimates small year classes in 2011,
2013, 2015, and 2018, and there is no information in the data to
estimate the sizes of the 2019 and 2020 year classes.
The Pacific whiting relative spawning stock is estimated to be
1.196 million mt, or 65 percent of unfished levels at the start of
2020. The estimated biomass has declined since 2017, during a time of
record catches and as the very large 2010 year class ages and mortality
surpasses increased production. Projections show that even in the
absence of fishing, the stock is expected to decline from 65 percent to
62 percent of unfished biomass.
The stock is considered healthy, and the joint probability that the
relative spawning stock biomass is both below 40 percent of unfished
level and that fishing mortality is above the relative fishing
intensity of the Agreement's F-40 percent default harvest rate is
estimated to be 4.3 percent.
2020 Pacific Whiting TAC Evaluation and Recommendation
NMFS considered information and recommendations from the Treaty's
JMC, JTC, SRG, AP, and the Council. The stock assessment from the JTC
and the SRG peer review are the best scientific information available
for determining the coastwide Pacific whiting TAC. NMFS heard testimony
from the AP and JMC at the March 2020 meeting. The Council discussed
Pacific whiting during its April 2020 meeting and did not make any
specific recommendations regarding the 2020 Pacific whiting TAC.
NMFS initially considered setting the TAC resulting from the
default harvest rate (666,458 mt) and all of the potential adjusted
coastwide TACs discussed during the AP and JMC March 2020 meeting. This
includes the U.S. initial (597,500 mt) and final positions (555,000
mt), and the Canadian initial (300,000 mt) and final positions (390,000
mt). However, because Canada's proposed TACs are well below the TACs
that support a sustainable whiting resource according to the stock
assessment and would have negative economic impact on the U.S. fleet
with little economic impact on Canada's fleet, we excluded them from
further consideration.
NMFS therefore evaluated coastwide TACs ranging from 555,000 mt to
666,458 mt in developing our proposed coastwide TAC of 575,000 mt. The
stock assessment supports that most of the TACs within this range would
provide adequate opportunity for both Canadian and U.S. fleets, while
sustainably managing the Pacific whiting resource.
Biological Impacts of Potential Whiting TAC Levels
The Act directs NMFS to use the default harvest rate set out in the
Agreement unless NMFS determines that a different rate is necessary to
sustain the offshore whiting resource. The Agreement specifies a
default harvest rate of ``F-40 percent'' which is the fishing mortality
rate that would reduce the relative spawning stock biomass, calculated
on a per recruit basis (a measure of stock reproductive potential) to
40 percent of what it would have been in the absence of fishing
mortality. Although there is not a default biomass level, the JMC,
since implementation of the Agreement, has focused on choosing a TAC
designed to prevent the relative spawning stock biomass from falling
below 40 percent of what it would have been in the absence of fishing
mortality, often called B40. NMFS will follow the same practice of
choosing a TAC designed to prevent the relative spawning stock biomass
from falling below this biomass level.
To determine the impact of a specific TAC on relative spawning
stock biomass, we applied an estimate of the Pacific whiting fleet's
utilization rate, the proportion of the TAC removed through fishing
effort, to the range of TACs we considered. Over the last ten years,
neither the U.S. nor the Canadian fleets have ever caught the entire
TAC. The 10-year (2010-2019) average utilization rate is 71.3 percent
of the coastwide TAC. The five-year average utilization rate from 2010-
2014 is higher (78.1 percent) than the ten-year average, while the 5-
year average utilization rate from 2015-2019 is lower (64.5 percent).
These averages provide a realistic range for projecting the utilization
rates in 2020 and 2021.
The stock assessment indicates that applying any of the estimated
average utilization rates to the range of coastwide TACs we considered
results in relative spawning stock biomass levels above B40 percent
after one fishing year (49-53 percent relative spawning stock biomass).
When applying these coastwide TACs for 2 years, a TAC of 666,458 mt
with the higher utilization rates at 71 percent or higher results in
relative spawning stock biomass levels below B40 percent (37 and 39
percent). Using the same approach, a coastwide TAC of 597,500 mt and
the highest utilization rate (78.08 percent) would also result in the
relative spawning stock biomass level to fall below B40 percent by the
beginning
[[Page 21374]]
of 2022. Although the Pacific whiting TAC is set annually and could be
adjusted after the 2021 stock assessment, the fact that these
projections result in spawning biomass levels below B40 percent after 2
years suggests that a TAC at the default harvest level and last year's
TAC (597,500 mt) may risk the sustainable management of the Pacific
whiting resource.
Using the same approach as described above, TACs of 575,000 mt and
555,000 mt combined with the highest utilization rate being considered,
result in a projected harvest of 448,960 mt and 433,344 mt,
respectively. The stock assessment indicates that these levels of
harvest in 2020 would result in an estimated relative spawning stock
biomass of 51 percent at the beginning of 2021, which is well above the
B40 percent level, and an estimated relative spawning stock biomass of
40--41 percent at the beginning of 2022.
Overall, the stock assessment indicates that the relative spawning
stock biomass of Pacific whiting has a high probability of being lower
at the beginning of 2021 than 2020, ranging from an 81 percent
probability with no harvest to a 97 percent probability at the default
harvest rate. Although a decline is probable even in the absence of
fishing pressure, the decline is relatively modest and does not
threaten the sustainability of the resource. At the actual harvest
rates under consideration the stock assessment indicates there is less
than 33 percent chance of relative spawning stock biomass falling below
B40 percent in 1 year, a less than 10 percent probability of falling
below B25 percent, and essentially no chance of falling below B10
percent after 1 year.
Continuing these harvest levels into a second year does have an
increased chance of relative spawning stock biomass falling below B40
percent. Two years of actual harvests above approximately 460,000 mt
result in a greater than 50 percent probability of falling below B40
percent, a 20 percent probability of falling below B25 percent, and a 4
percent probability of falling below B10 percent. The best scientific
information available indicates that reduction from last year's
coastwide TAC (597,500 mt), and deviation from the Act's default
harvest rate, would support the long-term sustainability of the stock.
Economic Impacts of Potential Pacific Whiting TAC Levels
The Pacific whiting fishery is the highest volume fishery on the
West Coast of the United States, providing hundreds of jobs. In 2019,
total revenue was estimated to be $29 million in the non-tribal
shoreside sector and $35 million in the at-sea whiting sector. The
total non-tribal ex-vessel revenue in 2019 is estimated to have been
about $64 million. This is higher than the 2015-2019 inflation-adjusted
average of approximately $54 million. Maintaining access to the Pacific
whiting resource is important for both direct fishery participants and
West Coast fishing communities.
The starting and ending proposals from Canada, 300,000 mt and
390,000 mt, represent a 49 percent and 35 percent reduction from the
2019 TAC, respectively. Reductions of this magnitude would have
negative economic impact on U.S. coastal communities. Canada's proposed
TACs reflect their concern with the declining Pacific whiting biomass
as the 2010 year class ages, as well as uncertainty of the recent
recruitment strength since the stock assessment is not able to predict
cohort strength until they are detected by the acoustic survey and
fishery. However, the stock assessment indicates that the higher TACs
proposed by the U.S. continue to provide a sustainable Pacific whiting
resource and result in the relative spawning stock biomass levels above
B40 percent after 1 year, and at or above B40 percent after 2 years of
fishing. Because of these factors, NMFS has preliminarily determined
that a large reduction is not appropriate but supports a measured
reduction from last year's TAC.
2020 Pacific Whiting Adjusted TAC Recommendation
The Act requires NMFS to make the necessary adjustments to the TAC
specified in the Agreement (Paragraph 5 of Article II). The Agreement
(Paragraph 5 of Article II) requires adjustments to the coastwide TAC
to account for overages if either U.S. or Canadian catch in the
previous year exceeded its individual TAC, or carryovers, if U.S. or
Canadian catch was less than its individual TAC in the previous year.
Both the U.S. and Canada harvested less than their individual TACs in
2019, and therefore carryover is applied to the 2020 individual TACs.
Taking into account the percentage shares for each country (26.12
percent for Canada and 73.88 percent for the U.S.) and the adjustments
for uncaught fish, as required by the Act, we recommend a final
adjusted coastwide TAC of 575,000 mt, with a final adjusted TAC for
Canada of 150,190 mt (129,822 mt + 20,367 mt carryover adjustment), and
a final adjusted TAC for the US of 424,810 mt (367,202 mt + 57,608 mt
carryover adjustment). This recommendation is consistent with the best
available scientific information, provisions of the Agreement, and the
Whiting Act.
Tribal Allocations
The regulations at 50 CFR 660.50(d) identify the procedures for
implementing the treaty rights that Pacific Coast treaty Indian tribes
have to harvest groundfish in their usual and accustomed fishing areas
in U.S. waters. Tribes with treaty fishing rights in the area covered
by the Pacific Coast Groundfish FMP request allocations, set-asides, or
regulations specific to the tribes during the Council's biennial
harvest specifications and management measures process. The regulations
state that the Secretary will develop tribal allocations and
regulations in consultation with the affected tribe(s) and, insofar as
possible, with tribal consensus.
NMFS allocates a portion of the U.S. TAC of Pacific whiting to the
tribal fishery, following the process established in 50 CFR 660.50(d).
The tribal allocation is subtracted from the U.S. Pacific whiting TAC
before allocation to the non-tribal sectors.
Four Washington coastal treaty Indian tribes including the Makah
Indian Tribe, Quileute Indian Tribe, Quinault Indian Nation, and the
Hoh Indian Tribe (collectively, the ``Treaty Tribes''), can participate
in the tribal Pacific whiting fishery. Tribal allocations of Pacific
whiting have been based on discussions with the Treaty Tribes regarding
their intent for those fishing years. The Hoh Tribe has not expressed
an interest in participating in the Pacific whiting fishery to date.
The Quileute Tribe and Quinault Indian Nation have expressed interest
in beginning to participate in the Pacific whiting fishery at a future
date. To date, only the Makah Tribe has prosecuted a tribal fishery for
Pacific whiting, and has harvested Pacific whiting since 1996 using
midwater trawl gear. Table 1 below provides a recent history of U.S.
TACs and annual tribal allocation in mt.
Table 1--U.S. Total Allowable Catch and Annual Tribal Allocation in
Metric Tons
------------------------------------------------------------------------
Tribal
Year U.S. TAC \1\ Allocation
(mt) (mt)
------------------------------------------------------------------------
2010.................................... 193,935 49,939
2011.................................... 290,903 66,908
2012.................................... 186,037 48,556
2013.................................... 269,745 63,205
2014.................................... 316,206 55,336
2015.................................... 325,072 56,888
2016.................................... 367,553 64,322
[[Page 21375]]
2017.................................... 441,433 77,251
2018.................................... 441,433 77,251
2019.................................... 441,433 77,251
------------------------------------------------------------------------
\1\ Beginning in 2012, the United States started using the term Total
Allowable Catch, or TAC, based on the Agreement between the Government
of the United States of America and the Government of Canada on
Pacific Hake/Whiting. Prior to 2012, the terms Optimal Yield (OY) and
ACL were used.
In 2009, NMFS, the states of Washington and Oregon, and the Treaty
Tribes started a process to determine the long-term tribal allocation
for Pacific whiting. However, these groups have not yet determined a
long-term allocation. In order to ensure Treaty Tribes continue to
receive allocations, this rule proposes the 2020 tribal allocation of
Pacific whiting. This allocation is not intended to set precedent for
future allocations.
In exchanges between NMFS and the Treaty Tribes during November and
December 2019, the Makah Tribe indicated their intent to participate in
the tribal Pacific whiting fishery in 2020 and requested 17.5 percent
of the U.S. TAC. The Quinault Indian Nation and Quileute Indian Tribe
both informed NMFS in December 2019 that they will not participate in
the 2020 fishery. The Hoh Indian Tribe has, in previous years,
indicated in conversations with NMFS that they have no plans to fish
for whiting in the foreseeable future and will contact NMFS if that
changes. NMFS will contact the Tribes during the proposed rule comment
period to refine the 2020 allocation before allocating the final U.S.
TAC between the tribal and non-tribal whiting fisheries. NMFS proposes
a tribal allocation that accommodates the Makah Tribe's request of 17.5
percent of the U.S. TAC. The proposed 2020 U.S.TAC is 424,810 mt, and
therefore the proposed 2020 tribal allocation is 74,342 mt. NMFS has
determined that the current scientific information regarding the
distribution and abundance of the coastal Pacific whiting stock
indicates the 17.5 percent is within the range of the tribal treaty
right to Pacific whiting.
Non-Tribal Research and Bycatch Set-Asides
The U.S. non-tribal whiting fishery is managed under the Council's
Pacific Coast Groundfish FMP. Each year, the Council recommends the
amount of Pacific whiting to accommodate incidental mortality of
Pacific whiting in research activities and non-groundfish fisheries
based on estimates of scientific research catch and estimated bycatch
mortality in non-groundfish fisheries. At its November 2019 meeting,
the Council recommended an incidental mortality set-aside of 1,500 mt
for 2020. This is consistent with the amount set-aside for research and
incidental mortality each year since 2014. This rule proposes the
Council's recommendations.
Non-Tribal Harvest Guidelines and Allocations
In addition to the tribal allocation, this proposed rule
establishes the fishery harvest guideline (HG), called the non-tribal
allocation. The proposed 2020 fishery HG for Pacific whiting is 348,968
mt. This amount was determined by deducting the 74,342 mt tribal
allocation and the 1,500 mt allocation for scientific research catch
and fishing mortality in non-groundfish fisheries from the total U.S.
TAC of 424,810 mt. The Council recommends the research and bycatch set-
aside on an annual basis, based on estimates of scientific research
catch and estimated bycatch mortality in non-groundfish fisheries. The
regulations further allocate the fishery HG among the three non-tribal
sectors of the Pacific whiting fishery: The catcher/processor (C/P)
Coop Program, the Mothership (MS) Coop Program, and the Shorebased
Individual Fishing Quota (IFQ) Program. The C/P Coop Program is
allocated 34 percent (118,649 mt for 2020), the MS Coop Program is
allocated 24 percent (83,752 mt for 2020), and the Shorebased IFQ
Program is allocated 42 percent (146,567 mt for 2020). The fishery
south of 42[deg] N lat. may not take more than 7,328 mt (5 percent of
the Shorebased IFQ Program allocation) prior to May 15, the start of
the primary Pacific whiting season north of 42[deg] N lat.
The environmental assessment for the 2019-2020 harvest
specifications rule (see Electronic Access) analyzed a range of TAC
alternatives for 2020, and the final 2020 TAC falls within this
analyzed range. In addition, via the 2019-2020 harvest specifications
rulemaking process, the public had an opportunity to comment on the
2019-2020 TACs for whiting, just as they did for all species in the
groundfish FMP. NMFS follows this process because, unlike for all other
groundfish species, the TAC for whiting is decided in a highly
abbreviated annual process from February through April of every year,
and the normal rulemaking process would not allow for the fishery to
open with the new TAC on the annual season opening date of May 15.
Table 2--2020 Proposed Pacific Whiting Allocations in Metric Tons
------------------------------------------------------------------------
2020 Pacific
whiting
Sector allocation
(mt)
------------------------------------------------------------------------
Tribal.................................................. 74,342
Catcher/Processor (C/P) Coop Program.................... 118,649
Mothership (MS) Coop Program............................ 83,752
Shorebased IFQ Program.................................. 146,567
------------------------------------------------------------------------
2020 Harvest Specifications for Pacific Coast Shortbelly Rockfish and
Cowcod South of 40[deg]10' N Latitude
Shortbelly rockfish and cowcod south of 40[deg]10' N latitude are
managed under the Pacific Coast Groundfish FMP. The FMP requires that
the Council set harvest specifications and management measures for
groundfish at least biennially. NMFS established 2019 and 2020 harvest
specifications including overfishing limits (OFLs), allowable
biological catches (ABCs), ACLs and management measures such as annual
catch targets (ACTs) for groundfish stocks in December 2018 (83 FR
63970, December 12, 2018). In June 2019, the Council and NMFS received
public comment from affected stakeholders that low catch limits for two
stocks, cowcod south of 40[deg]10' N latitude and shortbelly rockfish,
were preventing vessels from harvesting co-occurring healthy fish
stocks because of increased bycatch levels. The Council held meetings
in September and November 2019 to identify a range of alternatives for
each stock and select final preferred alternatives to recommend for
implementation. This proposed rule is based on the Council's final
recommendations made at its November 2019 meeting. The Council deemed
the proposed regulations consistent with and necessary to implement the
proposed actions in a March 19, 2020 letter. The Analysis identifies
the preferred alternatives and other decision points and is posted on
the NMFS West Coast Region web page (see ADDRESSES) along with this
proposed rule.
The Council and NMFS consider the proposed actions consistent with
provisions in the Pacific Coast Groundfish FMP, which allows changes to
the harvest specifications and adjustments to management measures on a
schedule other than the typical
[[Page 21376]]
biennial cycle under special circumstances.
Shortbelly Rockfish (Sebastes jordani)
This rule proposes to implement the Council recommendation from its
November 2019 meeting, to increase the 2020 ACL for shortbelly rockfish
to 3,000 mt. The remaining shortbelly rockfish catch limits for 2020,
including the OFL and ABC, are unchanged from those implemented in the
2019-2020 Pacific Coast Groundfish Biennial Harvest Specifications (83
FR 63970, December 12, 2018). The proposed changes are summarized in
Table 3 below.
Table 3--Comparison of No Action Alternative and Proposed 2020 Harvest
Specifications and Management Measures for Shortbelly Rockfish in Metric
Tons
------------------------------------------------------------------------
No action
alternative Proposed rule
(current 2020)
------------------------------------------------------------------------
OFL................................... 6,950 6,950
ABC................................... 5,789 5,789
ACL................................... 500 3,000
Fishery Harvest Guideline............. 483 2,983
------------------------------------------------------------------------
Shortbelly rockfish (Sebastes jordani) is one of the most abundant
rockfish species and an important forage species in the California
Current Ecosystem. Unlike most harvested Pacific coast rockfishes
(e.g., bocaccio and cowcod), shortbelly rockfish are small-bodied,
relatively short-lived and semi-pelagic rockfish that school as adults.
Shortbelly rockfish recruitment is highly variable among years, causing
populations to undergo large ``booms and busts''.
Historically, shortbelly rockfish was most abundant off central
California from Monterey Bay to Point Reyes, common in southern
California, and only rarely encountered north of Cape Mendocino,
California. In recent years, shortbelly rockfish distribution has
extended north of Cape Mendocino, California and into Oregon and
Washington waters, the principal fishing areas the midwater trawl
fishery operates in to harvest Pacific whiting. While shortbelly
rockfish bycatch was historically low in the Pacific whiting fishery,
the recent shift in distribution and a likely increase in abundance, is
resulting in increased bycatch of shortbelly rockfish in the Pacific
whiting midwater trawl fishery.
Shortbelly rockfish was last assessed in 2007. The assessment,
available on the Council's website at https://www.pcouncil.org/documents/2007/04/stock-assessment-model-for-the-shortbelly-rockfish-sebastes-jordani-in-the-california-current.pdf/, estimated the
shortbelly rockfish stock to be 67 percent of unfished levels at the
start of 2005. Given that the population size is known to be highly
dynamic, it is possible that the population size and distribution
changed in the recent years. The Analysis describes NMFS survey data,
including the Southwest Fisheries Science Center's Rockfish Recruitment
and Ecosystem Analysis Survey (RREAS) and California Cooperative
Oceanic Fisheries Investigations (CalCOFI) and the Northwest Fisheries
Science Center's West Coast Groundfish Bottom Trawl Survey. The data
show extraordinarily high recruitment events occurred between 2013 and
2017, and provide evidence that the overall shortbelly rockfish
population was very high in 2018-2019. The population size in southern
California remains close to average levels and suggests shortbelly
rockfish population did not simply shift to northern waters. Increased
encounters of shortbelly rockfish in northern midwater trawl fisheries
is likely the result of increased recruitment and coastwide biomass
coupled with an expansion of its geographic range on the West Coast.
In addition to examining NMFS survey data for trends in shortbelly
rockfish biomass and distribution, the Analysis describes that forage
species other than shortbelly rockfish (specifically northern anchovy)
were unusually abundant, and that there was higher than average
production of several marine predators in 2018-19.
Shortbelly rockfish is not targeted by west coast fisheries. Given
its importance as a forage species, the Council considered classifying
shortbelly rockfish as an ecosystem component species in the 2013-14
biennial management cycle following the revision of National Standard 1
guidelines. The Council decided to retain shortbelly rockfish as a
stock actively managed in the fishery in the Pacific Coast Groundfish
FMP, which requires that the Council set an OFL, ABC, and ACL for this
stock as part of the biennial harvest specifications process. The
shortbelly rockfish default harvest control rule is used to set the ACL
each biennial cycle. The current default harvest control rule is a
constant catch value intended to accommodate observed bycatch levels,
discourage targeting, and continue to protect the availability of
shortbelly rockfish as a forage species. The Council recommended a low
ACL of 50 mt in 2011-2012 Pacific Coast Groundfish Biennial Harvest
Specifications and Management Measures (76 FR 27508, May 11, 2011) to
discourage development of any targeted fishery, and accommodate
incidental bycatch of shortbelly rockfish, while allowing the remaining
harvestable surplus of the stock to be available as forage fish in the
ecosystem. The ACL was increased from 50 to 500 mt in the 2015-2016
Pacific Coast Groundfish Biennial Harvest Specifications and Management
Measures (80 FR 12567, March 10, 2015) to accommodate a potential
increase in bycatch as a midwater rockfish fishery re-emerged following
the rebuilding of widow rockfish.
Shortbelly rockfish catch remained low and well below the ACL of
500 mt until 2017 when it increased from 30 mt to 320 mt. The Analysis
describes annual catch of shortbelly rockfish. High bycatch of
shortbelly rockfish in the whiting sectors resulted in the fishery
exceeding the ACLs in 2018 (508 mt) and 2019 (approximately 655 mt).
In the absence of this proposed rule to increase the 2020
shortbelly rockfish ACL, a future shortbelly rockfish overage could
result in early closure of the Pacific whiting and non-whiting midwater
trawl fisheries, which could have negative economic consequences for
vessels, processors, and communities. The magnitude of economic losses
due to early fishery closure from attaining the shortbelly rockfish ACL
is difficult to project and is dependent on which fisheries would close
and when they would close. The Analysis describes impacts of potential
closures of the midwater trawl fisheries targeting whiting and pelagic
rockfish
[[Page 21377]]
that are most likely to incur a large bycatch of shortbelly rockfish
and be subject to an early closure if the shortbelly rockfish ACL is
attained. The range of predicted impacts in terms of foregone income is
$4.6 million to $175.2 million depending on whether there is a late
season closure in December or an earlier closure in June.
This action proposes changes to the shortbelly ACL are consistent
with Section 5.5.1 of the Pacific Coast Groundfish FMP, which states:
``. . .OFLs, ABCs, ACLs, OYs, ACTs, HGs, and quotas may only be
modified in cases where a harvest specification announced at the
beginning of the biennial fishing period is found to have resulted from
incorrect data or from computational errors. If the Council finds that
such an error has occurred, it may recommend the Secretary publish a
notice in the Federal Register revising the incorrect harvest
specification at the earliest possible date.''
The 2018 West Coast Groundfish Observer Program data and estimates
of shortbelly rockfish bycatch were not available when setting the 2019
and 2020 harvest specifications and this new information compels this
consideration.
Increasing the shortbelly rockfish ACL to 3,000 mt for the final
half of the 2020 fishing year would accommodate incidental bycatch of
the shortbelly rockfish stock given recent high bycatch in groundfish
trawl fisheries, while continuing to minimize bycatch, discourage
development of a targeted fishery for shortbelly rockfish, and
continuing to protect the availability of shortbelly rockfish as
important forage in the California Current Ecosystem.
The increase of the 2020 ACL is not anticipated to induce targeting
of shortbelly. Industry has indicated that shortbelly rockfish is not
currently marketable and does not expect it to become so in the near
future. The low ex-vessel price of $0.01-$0.03 per pound in recent
years supports industry reports that the fish is primarily used as
fishmeal or discarded at-sea. The median West Coast limited entry trawl
permitted vessel has variable operating costs of $0.46 per pound,
according to the most recent Economic Data Collection Report, and is
unlikely to pursue a targeting strategy for such a low value species,
as the revenues would be less than typical operating costs. Industry
also provided testimony that they avoid catching shortbelly rockfish
because the spines of shortbelly rockfish degrade Pacific whiting
quality as they are impinged in the codend.
The proposed rule continues to protect the availability of
shortbelly rockfish as important forage in the California Current
Ecosystem. Scientific information currently available provides evidence
of above average forage conditions in the California Current Ecosystem
with higher abundances of forage species such as anchovy and a high
overall shortbelly rockfish population in 2018-2019. Further, the
higher ACL under the proposed rule is well below the shortbelly
rockfish OFL of 6,950 mt, and ABC of 5,789 mt.
The proposed rule is an accountability measure that addresses the
operational issue of a low ACL that resulted in ACL overages in 2018
and 2019. National Standard 1 Guidelines state: ''On an annual basis,
the Council must determine as soon as possible after the fishing year
if an ACL was exceeded. If an ACL was exceeded, AMs must be implemented
as soon as possible to correct the operational issue that caused the
ACL overage, as well as any biological consequences to the stock or
stock complex resulting from the overage when it is known.''
The proposed increase would improve the performance and
effectiveness of the ACL by increasing the ACL to better correspond
with recent trends in shortbelly rockfish abundance and bycatch rates
in the groundfish fishery. This would reduce the risk of an ACL overage
in 2020, which would potentially close midwater trawl fisheries and
cause adverse economic impacts to West Coast fishing communities while
continuing to protect the availability of shortbelly rockfish as
important forage in the California Current Ecosystem.
Cowcod (Sebastes levis) South of 40[deg]10' N Latitude
This proposed rule would remove the cowcod ACT of 6 mt and reduce
the research catch set-aside to 1 mt for cowcod south of 40[deg]10' N.
latitude in 2020. The ACL would remain at 10 mt. The 2020 cowcod annual
vessel limit would increase from 858 pounds (.4 mt) to 1,264 pounds (.6
mt) for affected participants in the limited entry trawl fishery south
of 40[deg]10' N. latitude. The proposed changes are summarized in Table
4 below. This action would reduce the risk that vessels in the trawl
IFQ program reach their annual vessel limit for cowcod in 2020 and have
to cease fishing in the trawl IFQ program for the remainder of the
year.
Table 4--Summary of the Features of the No Action and Preferred Alternatives for Cowcod South of 40[deg]10' N
Latitude in Metric Tons, Except Where Noted as Pounds
----------------------------------------------------------------------------------------------------------------
No action alternative (current
2020) Proposed rule
----------------------------------------------------------------------------------------------------------------
OFL.................................... 76................................. 76
ABC.................................... 68................................. 68
ACL.................................... 10................................. 10
Research Set-aside..................... 2.................................. 1
Fishery HG............................. 8.................................. 9
ACT.................................... 6.................................. Removed
Non-Trawl Allocation (64 percent of the 3.8................................ 5.8
ACL).
Trawl Allocation (36 percent of the 2.2................................ 3.2
ACL).
Annual Vessel Limit (17.7 percent of 0.4 (858 pounds)................... 0.6 (1,264 pounds)
trawl allocation).
Increase in vessel limit............... 0.................................. 0.2 (406 pounds)
Increase in vessel limit (percent)..... 0.................................. 47
----------------------------------------------------------------------------------------------------------------
Updated information on cowcod research conducted by the Northwest
Fisheries Science Center and other entities indicates that a lower set-
aside will accommodate planned research activities without a risk of
exceeding the ACL.
Cowcod south of 40[deg]10' N latitude was declared overfished in
January 2000. In 2001, NMFS closed most of their habitat in the
Southern California Bight (SCB) south of Point Conception at 34[deg]27'
N latitude to bottom fishing. The Council adopted and NMFS implemented
a rebuilding plan for the
[[Page 21378]]
stock under Amendment 16-3 to the Pacific Coast Groundfish FMP (69 FR
57874, September 28, 2004), revised the rebuilding plan for the stock
under Amendment 16-4 in 2007 (71 FR 78638, December 29, 2006) and again
under Amendment 16-5 in 2011 (76 FR 77415, December 13, 2011). Using
the spawning potential ratio harvest control rate of 82.7 percent
specified in the most recent rebuilding plan, the median time to
rebuild was estimated to be 2068 at that time.
Harvest specifications and management measures for cowcod in the
2019-20 biennial management period were based on the 2013 rebuilding
analysis and consistent with the rebuilding plan provisions. Cowcod
stock assessments and rebuilding analyses are available on the
Council's website at https://www.pcouncil.org/stock-assessments-star-reports-stat-reports-rebuilding-analyses-terms-of-reference/groundfish-stock-assessment-documents/. The 2013 assessment and rebuilding
analysis concluded that the cowcod stock is rebuilding much more
quickly than anticipated under its rebuilding plan.
The 2020 cowcod harvest specifications and management measures were
established as part of the 2019-2020 Pacific Coast Groundfish Biennial
Harvest Specifications and Management Measures (83 FR 63970, December
12, 2018). The Stock Assessment and Fishery Evaluation (SAFE) document
posted on the Council's website at https://www.pcouncil.org/documents/2019/01/status-of-the-pacific-coast-groundfish-fishery-stock-assessment-and-fishery-evaluation-description-of-the-fishery-revised-january-2019.pdf/ contains a detailed description of cowcod, its status
and management, as well as the Council's Scientific and Statistical
Committee's approach for rebuilding analyses.
The Southwest Fisheries Science Center completed a new stock
assessment for cowcod in 2019 and the spawning stock depletion at the
start of 2019 is at 57 percent of unfished levels, which is above the
40 percent target. The 2019 stock assessment is available on the
Council's website at https://www.pcouncil.org/documents/2019/10/status-of-cowcod-sebastes-levis-in-2019-october-24-2019.pdf/. NMFS declared
the stock rebuilt effective September 30, 2019 in the 2019 Quarter 3
Status of the Stocks report available at https://www.fisheries.noaa.gov/national/population-assessments/fishery-stock-status-updates. As a result of the cowcod rebuilding, the Council and
NMFS will consider changes to cowcod catch limits in establishing the
2021-2022 Pacific Coast Groundfish Biennial Harvest Specifications and
Management Measures. This proposed rule does not consider a change to
the 2020 rebuilding harvest control rule. The ACL would remain at 10
mt.
To keep mortality of the stocks managed under the Pacific Coast
Groundfish FMP within the ACLs, the Council also recommends management
measures. Pacific Coast Groundfish FMP Section 6.2D describes the
process for modifying management measures, which includes a two Council
meeting process and a regulatory amendment. Management measures are
intended to rebuild overfished stocks, prevent catch from exceeding the
ACLs, and allow for the harvest of healthy stocks. The 2019-2020
Pacific Coast Groundfish Biennial Harvest Specifications and Management
Measures established an ACT of 6 mt for both 2019 and 2020 to address
the uncertainty in research impacts and ensure total mortality is
within the ACL. The ACT functions as a fishery harvest guideline and is
the amount allocated across groundfish trawl and non-trawl fisheries.
The current specifications allocated 2 mt of cowcod for research.
Updated information on cowcod research is now available and indicates
that a lower set-aside of 1 mt would accommodate planned research
activities. Over the past several years, cowcod harvest has
consistently been far below the ACL and ACT.
The Pacific Coast Groundfish Trawl Catch Share Program (75 FR
60868, October 1, 2010 and 75 FR 78343, December 15, 2010) issued IFQ
to limited entry trawl participants. In addition to IFQ, the program
established annual vessel limits for IFQ species to prevent any one
entity from having excessive control of a stock during a fishing year.
The 2020 cowcod annual vessel limit of 858 pounds (389.182 kg) is based
on an apportionment (17.7 percent) of the trawl allocation of the 6 mt
ACT (Table 3).
The low overall catch limits of cowcod have prevented the
Shorebased IFQ bottom trawlers from accessing healthy co-occurring
groundfish stocks and in some years have resulted in vessels ending
their fishing season early. Although the cowcod stock is now rebuilt,
the timing of the biennial groundfish specification cycle means that
the fleet would not benefit from less restrictive cowcod catch limits
until 2021. This proposed action would reduce the risk that vessels
fishing south of 40[deg]10' N lat. in the groundfish trawl IFQ program
would reach their annual vessel limit for cowcod in 2020 and have to
cease fishing in the trawl IFQ program for the remainder of the year,
which would result in severe adverse economic impacts for those vessels
and the fishing communities reliant on the trawl fishery south of
40[deg]10' N lat.
This proposed rule would be implemented under the statutory and
regulatory authority of section 304(b) and 305(d) of the Magnuson-
Stevens Act, and the Pacific Whiting Act of 2006. With this proposed
rule, NMFS, acting on behalf of the Secretary, would ensure that the
FMP is implemented in a manner consistent with treaty rights of four
Treaty Tribes to fish in their ``usual and accustomed grounds and
stations'' in common with non-tribal citizens. United States v.
Washington, 384 F. Supp. 313 (W.D. Wash. 1974).
III. Classification
NMFS notes that the public comment period for this proposed rule is
15 days. As a result of the requirements to amend reallocation
provisions and announce Pacific whiting harvest guidelines by the
Pacific whiting season start date, May 15th, NMFS has determined that a
15-day comment period best balances the interest in allowing the public
adequate time to comment on the proposed measures while implementing
the management measures and announcing the Pacific whiting allocations.
Pursuant to section 304 (b)(1)(A) and 305 (d) of the Magnuson-
Stevens Act, the NMFS Assistant Administrator has determined that this
proposed rule is consistent with the Pacific Coast Groundfish FMP,
other provisions of the Magnuson-Stevens Act, and other applicable law,
subject to further consideration after public comment. In making its
final determination, NMFS will take into account the complete record,
including the data, views, and comments received during the comment
period.
Pursuant to Executive Order 13175, this proposed rule was developed
after meaningful consultation and collaboration with tribal officials
from the area covered by the Pacific Coast Groundfish FMP. Under the
Magnuson-Stevens Act at 16 U.S.C. 1852(b)(5), one of the voting members
of the Pacific Council must be a representative of an Indian tribe with
federally recognized fishing rights from the area of the Council's
jurisdiction. In addition, regulations implementing the Pacific Coast
Groundfish FMP establish a procedure by which the tribes with treaty
fishing rights in the area covered by the Pacific Coast Groundfish FMP
request new allocations or regulations specific to the tribes, in
writing, before the first of the two meetings at which
[[Page 21379]]
the Council considers groundfish management measures. The regulations
at 50 CFR 660.324(d) further state, ``the Secretary will develop tribal
allocations and regulations under this paragraph in consultation with
the affected tribe(s) and, insofar as possible, with tribal
consensus.'' The tribal management measures in this proposed rule have
been developed following these procedures.
The Office of Management and Budget has determined that this
proposed rule is not significant for purposes of Executive Order 12866.
This proposed rule is not an Executive Order 13771 regulatory action
because this rule is not significant under Executive Order 12866.
The Council and NMFS prepared an Integrated Analysis for the
shortbelly rockfish and cowcod actions, which address the statutory
requirements of the Magnuson-Stevens Act, the National Environmental
Policy Act, Presidential Executive Order 12866, and the Regulatory
Flexibility Act. As part of this Analysis, an environmental assessment
(EA) was prepared that describes the impact on the human environment
that would result from implementation of the proposed shortbelly
rockfish action. The full suite of alternatives analyzed by the Council
can be found on the Council's website at www.pcouncil.org. This
Analysis does not contain all the alternatives because a range of
potential total harvest levels for Pacific whiting and cowcod, which
these actions would simply allocate among user groups, have been
considered under the Final Environmental Impact Statement for Harvest
Specifications and Management Measures for 2015-2016 and Biennial
Periods thereafter (2015/16 FEIS) and in the Environmental Assessment
for Harvest Specifications and Management Measures for 2019-2020 and
Biennial Periods Thereafter and is available from NMFS (see ADDRESSES).
The 2015/16 FEIS examined the harvest specifications and management
measures for 2015-16 and 10 year projections for routinely adjusted
harvest specifications and management measures. The 10 year projections
were produced to evaluate the impacts of the ongoing implementation of
harvest specifications and management measures and to evaluate the
impacts of the routine adjustments that are the main component of each
biennial cycle. Therefore, the EA for the 2019-20 cycle tiers from the
2015/16 FEIS and focuses on the harvest specifications and management
measures that were not within the scope of the 10 year projections in
the 2015/16 FEIS. A copy of the EA for shortbelly rockfish, which is
included as part of the Analysis, is available from NMFS (see
ADDRESSES). This action also announces a public comment period on the
EA for shortbelly rockfish.
Initial Regulatory Flexibility Analyses (IRFA) were prepared for
this action, as required by section 603 of the Regulatory Flexibility
Act (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, and the legal basis for this action is
contained in the SUMMARY section and at the beginning of the
SUPPLEMENTARY INFORMATION section of the preamble. A summary of the
IRFA follow. Copies of the IRFAs are available from NMFS (See
ADDRESSES).
Under the RFA, the term ``small entities'' includes small
businesses, small organizations, and small governmental jurisdictions.
The Small Business Administration has established size criteria for
entities involved in the fishing industry that qualify as small
businesses. A business involved in fish harvesting is a small business
if it is independently owned and operated and not dominant in its field
of operation (including its affiliates) and if it has combined annual
receipts, not in excess of $11 million for all its affiliated
operations worldwide (see 80 FR 81194, December 29, 2015). A wholesale
business servicing the fishing industry is a small business if it
employs 100 or fewer persons on a full time, part time, temporary, or
other basis, at all its affiliated operations worldwide. A seafood
processor is a small business if it is independently owned and
operated, not dominant in its field of operation, and employs 750 or
fewer persons on a full time, part time, temporary, or other basis, at
all its affiliated operations worldwide. For purposes of rulemaking,
NMFS is also applying the seafood processor standard to catcher
processors because Pacific whiting Catcher-Processors (C/Ps) earn the
majority of the revenue from processed seafood product.
Description and Estimate of the Number of Small Entities to Which the
Rule Applies, and Estimate of Economic Impacts by Entity Size and
Industry
This proposed rule would affect how Pacific whiting is allocated to
the following sectors/programs: Tribal, Shorebased IFQ Program Trawl
Fishery, MS Coop Program Whiting At-sea Trawl Fishery, and C/P Coop
Program Whiting At-sea Trawl Fishery. The amount of Pacific whiting
allocated to these sectors is based on the U.S. TAC. We expect one
tribal entity to fish for Pacific whiting in 2020. Tribes are not
considered small entities for the purposes of RFA. Impacts to tribes
are nevertheless considered in this analysis. As of January 2020, the
Shorebased IFQ Program is composed of 167 Quota Share permits/accounts
(134 of which were allocated whiting quota pounds), and 41 first
receivers, two of which are designated as whiting-only receivers and 15
that may receive both whiting and non-whiting. These regulations also
directly affect participants in the MS Co-op Program, a general term to
describe the limited access program that applies to eligible harvesters
and processors in the MS sector of the Pacific whiting at-sea trawl
fishery. This program currently consists of six MS processor permits,
and a catcher vessel fleet currently composed of a single co-op, with
34 Mothership/Catcher Vessel (MS/CV) endorsed permits (with three
permits each having two catch history assignments). These regulations
also directly affect the C/P Co-op Program, composed of 10 C/P endorsed
permits owned by three companies that have formed a single coop. These
co-ops are considered large entities from several perspectives; they
have participants that are large entities, and have in total more than
750 employees worldwide including affiliates. Although there are three
non-tribal sectors, many companies participate in two sectors and some
participate in all three sectors. As part of the permit application
processes for the non-tribal fisheries, based on a review of the Small
Business Administration size criteria, permit applicants are asked if
they considered themselves a ``small'' business, and they are asked to
provide detailed ownership information. Data on employment worldwide,
including affiliates, are not available for these companies, which
generally operate in Alaska as well as the West Coast and may have
operations in other countries as well. NMFS has limited entry permit
holders self-report size status. For 2020, all 10 CP permits reported
they are not small businesses, as did 8 mothership catcher vessels.
There is substantial, but not complete overlap between permit ownership
and vessel ownership so there may be a small number of additional small
entity vessel owners who will be impacted by this rule. After
accounting for cross participation, multiple QS account holders, and
affiliation through ownership, NMFS estimates that there are 106 non-
tribal entities directly affected by these proposed regulations, 85 of
which are considered ``small'' businesses.
[[Page 21380]]
This rule will allocate Pacific whiting between tribal and non-
tribal harvesters (a mixture of small and large businesses). Tribal
fisheries consist of a mixture of fishing activities that are similar
to the activities that non-tribal fisheries undertake. Tribal harvests
may be delivered to both shoreside plants and motherships for
processing. These processing facilities also process fish harvested by
non-tribal fisheries. The effect of the tribal allocation on non-tribal
fisheries will depend on the level of tribal harvests relative to their
allocation and the reapportionment process. If the tribes do not
harvest their entire allocation, there are opportunities during the
year to reapportion unharvested tribal amounts to the non-tribal
fleets. For example, in 2019 NMFS reapportioned 40,000 mt of the
original 77,251 mt tribal allocation. This reapportionment was based on
conversations with the tribes and the best information available at the
time, which indicated that this amount would not limit tribal harvest
opportunities for the remainder of the year. The reapportioning process
allows unharvested tribal allocations of Pacific whiting to be fished
by the non-tribal fleets, benefitting both large and small entities.
The revised Pacific whiting allocations for 2019 following the
reapportionment were: Tribal 37,251 mt, C/P Co-op 136,912 mt; MS Co-op
96,644 mt; and Shorebased IFQ Program 169,126 mt.
The prices for Pacific whiting are largely determined by the world
market because most of the Pacific whiting harvested in the U.S. is
exported. The U.S. Pacific whiting TAC is highly variable, as have
subsequent harvests and ex-vessel revenues. For the years 2015 to 2019,
the total Pacific whiting fishery (tribal and non-tribal) averaged
harvests of approximately 281,205 mt annually. The 2019 U.S. non-tribal
fishery had a catch of approximately 312,500 mt, and the tribal fishery
landed approximately 4,000 mt.
Impacts to Makah catcher vessels who elect to participate in the
tribal fishery are measured with an estimate of ex-vessel revenue. In
lieu of more complete information on tribal deliveries, total ex-vessel
revenue is estimated with the 2019 average shoreside ex-vessel price of
Pacific whiting, which was $200 per mt. At that price, the proposed
2020 tribal allocation of 74,342 mt would have an ex-vessel value of
$14.9 million.
Shortbelly Rockfish
The proposed rule would primarily affect limited entry trawl
vessels, especially midwater trawl vessels targeting Pacific whiting
and semi-pelagic rockfish (i.e., non-whiting) north of 40[deg]10' N
latitude given the sectors and gear experiencing the highest bycatch of
shortbelly rockfish in recent years. The entities fishing for Pacific
whiting (described in detail above), and the 14-20 vessels fishing in
the non-whiting midwater trawl fishery in 2017-2018, would be affected.
The preferred shortbelly rockfish alternative would have neutral to
positive impacts for limited entry trawl participants fishing in the
Pacific whiting and non-whiting midwater fisheries.
Cowcod South of 40[deg]10' N Latitude
The proposed rule would directly impact two groups: Quota share
owners of cowcod south of 40[deg]10' N latitude and catcher vessel
owners who operate vessels south of 40[deg]10' N latitude and have the
potential to encounter cowcod. There are 62 entities that own 2020
cowcod quota and 7 vessels that caught cowcod south of 40[deg]10' N.
latitude in 2019 that would be impacted by this rule. The preferred
cowcod alternative would have neutral to positive impacts for limited
entry trawl participants who own quota for this species and/or fish
south of 40[deg]10' N latitude. Quota owners that are able to sell
increased quota amounts may benefit. Most IFQ vessels do not operate
south of 40[deg]10' N latitude and would experience no impacts from the
preferred alternative.
A Description of any Significant Alternatives to the Proposed Rule That
Accomplish the Stated Objectives of Applicable Statutes and That
Minimize any Significant Economic Impact of the Proposed Rule on Small
Entities
NMFS considered two alternatives for the Pacific whiting action:
The ``No Action'' and the ``Proposed Action.'' NMFS considered a range
of alternatives for the Pacific whiting coastwide TAC. A coastwide TAC
of 555,000 mt has greater economic impacts for 2020 than what is
proposed is this rule (a coastwide TAC of 575,000 mt). Higher coastwide
TACs considered in the range (597,500 mt and 666,480 mt) would have
less economic impact for 2020. However, 2020 assessment projections
indicate these higher catch levels may result in near-term stock
biomass declines below target levels. This is contrary to the Whiting
Act and Agreement, which requires sustainable management of the Pacific
whiting resource.
NMFS did not consider a broader range of alternatives to the
proposed tribal allocation. The tribal allocation is based primarily on
the requests of the tribes. These requests reflect the level of
participation in the fishery that will allow them to exercise their
treaty right to fish for Pacific whiting. Under the Proposed Action
alternative, NMFS proposes to set the tribal allocation percentage at
17.5 percent, as requested by the Tribes. This would yield a tribal
allocation of 74,342 mt for 2020. Consideration of a percentage lower
than the tribal request of 17.5 percent is not appropriate in this
instance. As a matter of policy, NMFS has historically supported the
harvest levels requested by the Tribes. Based on the information
available to NMFS, the tribal request is within their tribal treaty
rights. A higher percentage would arguably also be within the scope of
the treaty right. However, a higher percentage would unnecessarily
limit the non-tribal fishery.
Under the no action alternative, NMFS would not set a coastwide TAC
or make an allocation to the tribal sector. This alternative was
considered, but the Act requires the U.S. to establish TACs to
sustainably manage the Pacific whiting resource. The regulatory
framework provides for a tribal allocation on an annual basis only.
Therefore, the no action alternative would result in no allocation of
Pacific whiting to the tribal sector in 2020, which would be
inconsistent with NMFS' responsibility to manage the fishery consistent
with the tribes' treaty rights. Given that there is a tribal request
for allocation in 2020, this alternative received no further
consideration.
Shortbelly Rockfish
The Council and NMFS considered three alternatives for shortbelly
rockfish: No action, specifying a 2020 ACL of 3,000 mt and specifying a
2020 ACL of 4,184 mt. Under the no action alternative, NMFS would not
change the 2020 ACL for shortbelly rockfish. This no action alternative
has the highest risk of an early fishery closure and lost revenue for
Pacific whiting and LE non-whiting midwater trawl fisheries and
communities. The range of predicted impacts in terms of foregone income
is $4.6 million to $175.2 million depending on whether there is a late
season closure in December or an earlier closure in June.
The proposed measure for shortbelly rockfish would reduce the risk
of an early closure for midwater trawl fisheries due to the possibility
of high bycatch of shortbelly rockfish in 2020, and avoid the adverse
economic impacts to West Coast fishing communities that would result
from such closures or constraints. The proposed measure to establish
the 2020 ACL at 3,000 mt rather than the alternative of 4,184 mt,
[[Page 21381]]
should be sufficient to avoid constraining the midwater trawl fishery
while continuing to ensure more than adequate shortbelly rockfish as
forage.
Cowcod
The Council and NMFS considered no action and alternatives to
provide relief on limited entry trawl participants fishing south of
40[deg]10' N latitude, including removing the ACT and adjustments to
the research set-aside amounts. Under the no action alternative, NMFS
would not change the ACT or research set-aside amounts. This no action
alternative would result in potential loss of revenue if vessels reach
their cowcod individual vessel limit and are required to cease fishing
for the remainder of the year.
The proposed measure for cowcod would eliminate the 2020 ACT of 6
mt for cowcod south of 40[deg]10' N latitude and reduce the research
set-aside amount to 1 mt. The annual vessel limit for cowcod would
increase from 858 lbs (.4 mt) to 1,264 lbs (.6 mt). This alternative
meets the stated purpose and need to reduce the risk that IFQ vessels
south of 40[deg]10' N latitude will reach their individual vessel
limits of cowcod in 2020 and have to cease fishing in the IFQ fishery
for the remainder of the year, which would result in adverse economic
impacts on those vessels and fishing communities in the area. The
Council considered an alternative to remove the ACT of 6 mt and reduce
the research set-aside to 0.5 mt. This alternative may have resulted in
a lesser economic impact on vessels and fishing communities, but it did
not provide an adequate amount of cowcod for research.
Regulatory Flexibility Act (RFA) Determination of No Significant Impact
NMFS determined this proposed rule would not adversely affect small
entities. The reapportioning process allows unharvested tribal
allocations of Pacific whiting, fished by small entities, to be fished
by the non-tribal fleets, benefitting both large and small entities.
The shortbelly and cowcod measures will assist small entities by
reducing the risk of early closures due to bycatch. The shortbelly
rockfish and cowcod measures are temporary and will be in effect for
less than 1 year.
NMFS has prepared IRFAs and is requesting comments on this
conclusion. See ADDRESSES.
There are no reporting, recordkeeping or other compliance
requirements in the proposed rule.
No Federal rules have been identified that duplicate, overlap, or
conflict with this action.
List of Subjects in 50 CFR Part 660
Fisheries, Fishing, Indian Fisheries.
Dated: April 13, 2020.
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 660 is
proposed to be 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. 660.50, revise paragraph (f)(4) to read as follows:
Sec. 660.50 Pacific Coast treaty Indian fisheries.
* * * * *
(f) * * *
(4) Pacific whiting. The tribal allocation for 2020 will be 74,342
mt.
* * * * *
0
3. Revise table 2a to part 660, subpart C, to read as follows:
Table 2a to Part 660, Subpart C--2020, and Beyond, Specification of OFL, ABC, ACL, ACT and Fishery Harvest
Guidelines
[Weights in metric tons]
----------------------------------------------------------------------------------------------------------------
Stocks/stock complexes Area OFL ABC ACL \a\ Fishery HG \b\
----------------------------------------------------------------------------------------------------------------
COWCOD \c\........................... S of 40[deg]10' N lat........ 76 68 10 9
COWCOD............................... (Conception)................. 62 57 NA NA
COWCOD............................... (Monterey)................... 13 11 NA NA
YELLOWEYE ROCKFISH \d\............... Coastwide.................... 84 77 49 43
Arrowtooth Flounder \e\.............. Coastwide.................... 15,306 12,750 12,750 10,655
Big Skate \f\........................ Coastwide.................... 541 494 494 452
Black Rockfish \g\................... California (S of 42[deg] N 341 326 326 325
lat.).
Black Rockfish \h\................... Washington (N of 46[deg]16' N 311 297 297 279
lat.).
Bocaccio \i\......................... S of 40[deg]10' N lat........ 2,104 2,011 2,011 1,965
Cabezon \j\.......................... California (S of 42[deg] N 153 146 146 146
lat.).
California Scorpionfish \k\.......... S of 34[deg]27' N lat........ 331 307 307 305
Canary Rockfish \l\.................. Coastwide.................... 1,431 1,368 1,368 1,301
Chilipepper Rockfish \m\............. S of 40[deg]10' N lat........ 2,521 2,410 2,410 2,325
Darkblotched Rockfish \n\............ Coastwide.................... 853 815 815 781
Dover Sole[deg]...................... Coastwide.................... 92,048 87,998 50,000 48,404
English Sole \p\..................... Coastwide.................... 11,101 10,135 10,135 9,919
Lingcod \q\.......................... N of 40[deg]10' N lat........ 4,768 4,558 4,541 4,263
Lingcod \r\.......................... S of 40[deg]10' N lat........ 977 934 869 858
Longnose Skate \s\................... Coastwide.................... 2,474 2,365 2,000 1,852
Longspine Thornyhead \t\............. N of 34[deg]27' N lat........ 3,901 3,250 2,470 2,420
Longspine Thornyhead \u\............. S of 34[deg]27' N lat........ ........ ....... 780 779
Pacific Cod \v\...................... Coastwide.................... 3,200 2,221 1,600 1,094
Pacific Whiting \w\.................. Coastwide.................... 666,458 ( \w\) ( \w\) 348,968
Pacific Ocean Perch \x\.............. N of 40[deg]10' N lat........ 4,632 4,229 4,229 4,207
Petrale Sole \y\..................... Coastwide.................... 2,976 2,845 2,845 2,524
Sablefish \z\........................ N of 36[deg] N lat........... 8,648 7,896 5,723 See Table 2c
Sablefish \aa\....................... S of 36[deg] N lat........... ........ ....... 2,032 2,028
Shortbelly Rockfish \bb\............. Coastwide.................... 6,950 5,789 3,000 2,983
Shortspine Thornyhead \cc\........... N of 34[deg]27' N lat........ 3,063 2,551 1,669 1,604
Shortspine Thornyhead \dd\........... S of 34[deg]27' N lat........ ........ ....... 883 882
[[Page 21382]]
Spiny Dogfish \ee\................... Coastwide.................... 2,472 2,059 2,059 1,726
Splitnose Rockfish \ff\.............. S of 40[deg]10' N lat........ 1,810 1,731 1,731 1,714
Starry Flounder \gg\................. Coastwide.................... 652 452 452 433
Widow Rockfish \hh\.................. Coastwide.................... 11,714 11,199 11,199 10,951
Yellowtail Rockfish \ii\............. N of 40[deg]10' N lat........ 6,261 5,986 5,986 4,941
Black Rockfish/Blue Rockfish/Deacon Oregon (Between 46[deg]16' N 670 611 611 609
Rockfish \jj\. lat. and 42[deg] N lat.).
Cabezon/Kelp Greenling \kk\.......... Oregon (Between 46[deg]16' N 216 204 204 204
lat. and 42[deg] N lat.).
Cabezon/Kelp Greenling \ll\.......... Washington (N of 46[deg]16' N 12 10 10 10
lat.).
Nearshore Rockfish \mm\.............. N of 40[deg]10' N lat........ 92 82 82 79
Shelf Rockfish \nn\.................. N of 40[deg]10' N lat........ 2,302 2,048 2,048 1,971
Slope Rockfish \oo\.................. N of 40[deg]10' N lat........ 1,873 1,732 1,732 1,651
Nearshore Rockfish \pp\.............. S of 40[deg]10' N lat........ 1,322 1,165 1,163 1,159
Shelf Rockfish \qq\.................. S of 40[deg]10' N lat........ 1,919 1,626 1,625 1,546
Slope Rockfish \rr\.................. S of 40[deg]10' N lat........ 855 743 743 723
Other Flatfish \ss\.................. Coastwide.................... 8,202 6,041 6,041 5,792
Other Fish \tt\...................... Coastwide.................... 286 239 239 230
----------------------------------------------------------------------------------------------------------------
\a\ Annual catch limits (ACLs), annual catch targets (ACTs) and harvest guidelines (HGs) are specified as total
catch values.
\b\ Fishery HGs means the HG or quota after subtracting Pacific Coast treaty Indian tribes allocations and
projected catch, projected research catch, deductions for fishing mortality in non-groundfish fisheries, and
deductions for EFPs from the ACL or ACT.
\c\ Cowcod south of 40[deg]10' N lat. 1 mt is deducted from the ACL to accommodate EFP fishing (less than 0.1
mt) and research activity, resulting in a fishery HG of 9 mt. Any additional mortality in research activities
will be deducted from the ACL.
\d\ Yelloweye rockfish. The 49 mt ACL is based on the current rebuilding plan with a target year to rebuild of
2029 and an SPR harvest rate of 65 percent. 6.1 mt is deducted from the ACL to accommodate the Tribal fishery
(2.3 mt), the incidental open access fishery (0.62 mt), EFP catch (0.24 mt) and research catch (2.92 mt),
resulting in a fishery HG of 43 mt. The non-trawl HG is 39.5 mt. The non-nearshore HG is 2.1 mt and the
nearshore HG is 6.2 mt. Recreational HGs are: 10.2 mt (Washington); 9.1 mt (Oregon); and 11.9 mt (California).
In addition, there are the following ACTs: Non-nearshore (1.7 mt), nearshore (4.9 mt), Washington recreational
(8.1 mt), Oregon recreational (7.2 mt), and California recreational (9.4 mt).
\e\ Arrowtooth flounder. 2,094.9 mt is deducted from the ACL to accommodate the Tribal fishery (2,041 mt), the
incidental open access fishery (40.8 mt), EFP fishing (0.1 mt), and research catch (13 mt), resulting in a
fishery HG of 10,655 mt.
\f\ Big skate. 41.9 mt is deducted from the ACL to accommodate the Tribal fishery (15 mt), the incidental open
access fishery (21.3 mt), EFP fishing (0.1 mt), and research catch (5.5 mt), resulting in a fishery HG of 452
mt.
\g\ Black rockfish (California). 1.3 mt is deducted from the ACL to accommodate EFP fishing (1.0 mt) and the
incidental open access fishery (0.3 mt), resulting in a fishery HG of 325 mt.
\h\ Black rockfish (Washington). 18.1 mt is deducted from the ACL to accommodate the Tribal fishery (18 mt) and
research catch (0.1 mt), resulting in a fishery HG of 279 mt.
\i\ Bocaccio south of 40[deg]10' N lat. The stock is managed with stock-specific harvest specifications south of
40[deg]10' N lat. and within the Minor Shelf Rockfish complex north of 40[deg]10' N lat. 46.1 mt is deducted
from the ACL to accommodate the incidental open access fishery (0.5 mt), EFP catch (40 mt) and research catch
(5.6 mt), resulting in a fishery HG of 1,965 mt. The California recreational fishery has an HG of 827.2 mt.
\j\ Cabezon (California). 0.3 mt is deducted from the ACL to accommodate the incidental open access fishery,
resulting in a fishery HG of 146 mt.
\k\ California scorpionfish south of 34[deg]27' N lat. 2.4 mt is deducted from the ACL to accommodate the
incidental open access fishery (2.2 mt) and research catch (0.2 mt), resulting in a fishery HG of 305 mt.
\l\ Canary rockfish. 67.1 mt is deducted from the ACL to accommodate the Tribal fishery (50 mt), the incidental
open access fishery (1.3 mt), EFP catch (8 mt), and research catch (7.8 mt), resulting in a fishery HG of
1,301 mt. Recreational HGs are: 44.3 mt (Washington); 66.5 mt (Oregon); and 119.7 mt (California).
\m\ Chilipepper rockfish south of 40[deg]10' N lat. Chilipepper are managed with stock-specific harvest
specifications south of 40[deg]10'N lat. and within the Minor Shelf Rockfish complex north of 40[deg]10' N
lat. 84.9 mt is deducted from the ACL to accommodate the incidental open access fishery (11.5 mt), EFP fishing
(60 mt), and research catch (13.4 mt), resulting in a fishery HG of 2,325 mt.
\n\ Darkblotched rockfish. 33.8 mt is deducted from the ACL to accommodate the Tribal fishery (0.2 mt), the
incidental open access fishery (24.5 mt), EFP catch (0.6 mt), and research catch (8.5 mt) resulting in a
fishery HG of 781 mt.
\o\Dover sole. 1,595.6 mt is deducted from the ACL to accommodate the Tribal fishery (1,497 mt), the incidental
open access fishery (49.3 mt), EFP fishing (0.1 mt), and research catch (49.2 mt), resulting in a fishery HG
of 48,404 mt.
\p\ English sole. 216.2 mt is deducted from the ACL to accommodate the Tribal fishery (200 mt), the incidental
open access fishery (8.1 mt), EFP fishing (0.1 mt), and research catch (8 mt), resulting in a fishery HG of
9,919 mt.
\q\ Lingcod north of 40[deg]10' N lat. 278 mt is deducted from the ACL for the Tribal fishery (250 mt), the
incidental open access fishery (9.8 mt), EFP catch (1.6 mt) and research catch (16.6 mt), resulting in a
fishery HG of 4,263 mt.
\r\ Lingcod south of 40[deg]10' N lat. 11.3 mt is deducted from the ACL to accommodate the incidental open
access fishery (8.1 mt) and research catch (3.2 mt), resulting in a fishery HG of 858 mt.
\s\ Longnose skate. 148.3 mt is deducted from the ACL to accommodate the Tribal fishery (130 mt), incidental
open access fishery (5.7 mt), EFP catch (0.1 mt), and research catch (12.5 mt), resulting in a fishery HG of
1,852 mt.
\t\ Longspine thornyhead. 50.4 mt is deducted from the ACL to accommodate the Tribal fishery (30 mt), the
incidental open access fishery (6.2 mt), and research catch (14.2 mt), resulting in a fishery HG of 2,420 mt.
\u\ Longspine thornyhead south of 34[deg]27' N lat. 1.4 mt is deducted from the ACL to research catch, resulting
in a fishery HG of 779 mt.
\v\ Pacific cod. 506.2 mt is deducted from the ACL to accommodate the Tribal fishery (500 mt), EFP catch (0.1
mt), research catch (5.5 mt), and the incidental open access fishery (0.6 mt), resulting in a fishery HG of
1,094 mt.
\w\ Pacific whiting. The 2020 OFL of 666,458 mt is based on the 2020 assessment with an F40% of FMSY proxy. The
proposed 2020 coastwide adjusted Total Allowable Catch (TAC) is 575,000 mt. The U.S. TAC is 73.88 percent of
the coastwide TAC. The proposed 2020 adjusted U.S. TAC is 424,810 mt (367,202 mt unadjusted TAC + 57,608 mt
carryover adjustment). From the adjusted U.S. TAC, 74,342 mt is deducted to accommodate the Tribal fishery,
and 1,500 mt is deducted to accommodate research and bycatch in other fisheries, resulting in a 2020 fishery
HG of 348,968 mt. The TAC for Pacific whiting is established under the provisions of the Agreement with Canada
on Pacific Hake/Whiting and the Pacific Whiting Act of 2006, 16 U.S.C. 7001-7010, and the international
exception applies. Therefore, no ABC or ACL values are provided for Pacific whiting.
\x\ Pacific ocean perch north of 40[deg]10' N lat. 22.4 mt is deducted from the ACL to accommodate the Tribal
fishery (9.2 mt), the incidental open access fishery (10 mt), EFP fishing (0.1 mt), and research catch (3.1
mt)-resulting in a fishery HG of 4,207 mt.
[[Page 21383]]
\y\ Petrale sole. 320.6 mt is deducted from the ACL to accommodate the Tribal fishery (290 mt), the incidental
open access fishery (6.4 mt), EFP catch (0.1 mt), and research catch (24.1 mt), resulting in a fishery HG of
2,524 mt.
\z\ Sablefish north of 36[deg] N lat. The 40-10 adjustment is applied to the ABC to derive a coastwide ACL value
because the stock is in the precautionary zone. This coastwide ACL value is not specified in regulations. The
coastwide ACL value is apportioned north and south of 36[deg] N lat., using the 2003-2014 average estimated
swept area biomass from the NMFS NWFSC trawl survey, with 73.8 percent apportioned north of 36[deg] N lat. and
26.2 percent apportioned south of 36[deg] N lat. The northern ACL is 5,723 mt and is reduced by 572 mt for the
Tribal allocation (10 perceN of the ACL north of 36[deg] N lat.). The 572 mt Tribal allocation is reduced by
1.5 percent to account for discard mortality. Detailed sablefish allocations are shown in Table 2c.
\aa\ Sablefish south of 36[deg] N lat. The ACL for the area south of 36[deg] N lat. is 2,032 mt (26.2 percent of
the calculated coastwide ACL value). 4.2 mt is deducted from the ACL to accommodate the incidental open access
fishery (1.8 mt) and research catch (2.4 mt), resulting in a fishery HG of 2,028 mt.
\bb\ Shortbelly rockfish. 17.2 mt is deducted from the ACL to accommodate the incidental open access fishery
(8.9 mt), EFP catch (0.1 mt), and research catch (8.2 mt), resulting in a fishery HG of 2,983 mt.
\cc\ Shortspine thornyhead north of 34[deg]27' N lat. 65.3 mt is deducted from the ACL to accommodate the Tribal
fishery (50 mt), the incidental open access fishery (4.7 mt), EFP catch (0.1 mt), and research catch (10.5
mt), resulting in a fishery HG of 1,604 mt for the area north of 34[deg]27' N lat.
\dd\ Shortspine thornyhead south of 34[deg]27' N lat. 1.2 mt is deducted from the ACL to accommodate the
incidental open access fishery (0.5 mt) and research catch (0.7 mt), resulting in a fishery HG of 882 mt for
the area south of 34[deg]27' N lat.
\ee\ Spiny dogfish. 333 mt is deducted from the ACL to accommodate the Tribal fishery (275 mt), the incidental
open access fishery (22.6 mt), EFP catch (1.1 mt), and research catch (34.3 mt), resulting in a fishery HG of
1,726 mt.
\ff\ Splitnose rockfish south of 40[deg]10' N lat. Splitnose rockfish in the north is managed in the Slope
Rockfish complex and with stock-specific harvest specifications south of 40[deg]10' N lat. 16.6 mt is deducted
from the ACL to accommodate the incidental open access fishery (5.8 mt), research catch (9.3 mt) and EFP catch
(1.5 mt), resulting in a fishery HG of 1,714 mt.
\gg\ Starry flounder. 18.8 mt is deducted from the ACL to accommodate the Tribal fishery (2 mt), EFP catch (0.1
mt), research catch (0.6 mt), and the incidental open access fishery (16.1 mt), resulting in a fishery HG of
433 mt.
\hh\ Widow rockfish. 248.4 mt is deducted from the ACL to accommodate the Tribal fishery (200 mt), the
incidental open access fishery (3.1 mt), EFP catch (28 mt) and research catch (17.3 mt), resulting in a
fishery HG of 10,951 mt.
\ii\ Yellowtail rockfish north of 40[deg]10' N lat. 1,045.1 mt is deducted from the ACL to accommodate the
Tribal fishery (1,000 mt), the incidental open access fishery (4.5 mt), EFP catch (20 mt) and research catch
(20.6 mt), resulting in a fishery HG of 4,941 mt.
\jj\ Black rockfishBlue rockfishDeacon rockfish (Oregon). 1.2 mt is deducted from the ACL to accommodate the
incidental open access fishery (0.3 mt) and EFP catch (0.9 mt), resulting in a fishery HG of 609 mt.
\kk\ CabezonKelp greenling (Oregon). 0.2 mt is deducted from the ACL to accommodate EFP catch, resulting in a
fishery HG of 204 mt.
\ll\ CabezonKelp greenling (Washington). There are no deductions from the ACL so the fishery HG is equal to the
ACL of 10 mt.
\mm\ Nearshore Rockfish north of 40[deg]10' N lat. 2.8 mt is deducted from the ACL to accommodate the Tribal
fishery (1.5 mt), EFP catch (0.1 mt), research catch (0.3), and the incidental open access fishery (0.9 mt),
resulting in a fishery HG of 79 mt.
\nn\ Shelf Rockfish north of 40[deg]10' N lat. 76.9 mt is deducted from the ACL to accommodate the Tribal
fishery (30 mt), the incidental open access fishery (17.7 mt), EFP catch (4.5 mt), and research catch (24.7
mt), resulting in a fishery HG of 1,971 mt.
\oo\ Slope Rockfish north of 40[deg]10' N lat. 80.8 mt is deducted from the ACL to accommodate the Tribal
fishery (36 mt), the incidental open access fishery (21.7 mt), EFP catch (1.5 mt), and research catch (21.6
mt), resulting in a fishery HG of 1,651 mt.
\pp\ Nearshore Rockfish south of 40[deg]10' N lat. 4.1 mt is deducted from the ACL to accommodate the incidental
open access fishery (1.4 mt) and research catch (2.7 mt), resulting in a fishery HG of 1,159 mt.
\qq\ Shelf Rockfish south of 40[deg]10' N lat. 79.1 mt is deducted from the ACL to accommodate the incidental
open access fishery (4.6 mt), EFP catch (60 mt), and research catch (14.5 mt), resulting in a fishery HG of
1,546 mt.
\rr\ Slope Rockfish south of 40[deg]10' N lat. 20.2 mt is deducted from the ACL to accommodate the incidental
open access fishery (16.9 mt), EFP catch (1 mt), and research catch (2.3 mt), resulting in a fishery HG of 723
mt. Blackgill rockfish has a stock-specific HG for the entire groundfish fishery south of 40[deg]10' N lat.
set equal to the species' contribution to the 40-10-adjusted ACL. Harvest of blackgill rockfish in all
groundfish fisheries south of 40[deg]10' N lat. counts against this HG of 159 mt.
\ss\ Other Flatfish. The Other Flatfish complex is comprised of flatfish species managed in the PCGFMP that are
not managed with stock-specific OFLs/ABCs/ACLs. MoS of the species in the Other Flatfish complex are
unassessed and include: butter sole, curlfin sole, flathead sole, Pacific sanddab, rock sole, sand sole, and
rex sole. 249.5 mt is deducted from the ACL to accommodate the Tribal fishery (60 mt), the incidental open
access fishery (161.6 mt), EFP fishing (0.1 mt), and research catch (27.8 mt), resulting in a fishery HG of
5,792 mt.
\tt\ Other Fish. The Other Fish complex is comprised of kelp greenling off California and leopard shark
coastwide. 8.9 mt is deducted from the ACL to accommodate the incidental open access fishery (8.8 mt) and
research catch (0.1 mt), resulting in a fishery HG of 230 mt.
0
4. Revise table 2b to part 660, subpart C, to read as follows:
Table 2b to Part 660, Subpart C--2020, and Beyond, Allocations by Species or Species Group
[Weight in metric tons]
--------------------------------------------------------------------------------------------------------------------------------------------------------
Trawl Non-trawl
Stocks/stock complexes Area Fishery HG or ---------------------------------------------------------------
ACT \a\ \b\ % Mt % Mt
--------------------------------------------------------------------------------------------------------------------------------------------------------
Arrowtooth flounder....................... Coastwide................... 10,655.1 95 10,122.3 5 532.8
Big skate \a\............................. Coastwide................... 452.1 95 429.5 5 22.6
Bocaccio \a\.............................. S of 40[deg]10' N lat....... 1,964.9 39 767.1 61 1,197.8
Canary rockfish \a\ \b\................... Coastwide................... 1,300.9 72 940.3 28 360.6
Chilipepper rockfish...................... S of 40[deg]10' N lat....... 2,325.1 75 1,743.8 25 581.3
COWCOD \a\................................ S of 40[deg]10' N lat....... 9.0 36 3.2 64 5.8
Darkblotched rockfish \c\................. Coastwide................... 781.2 95 742.1 5 39.1
Dover sole................................ Coastwide................... 48,404.4 95 45,984.2 5 2,420.2
English sole.............................. Coastwide................... 9,918.8 95 9,422.9 5 495.9
Lingcod................................... N of 40'10[deg] N lat....... 4,263.0 45 1,918.4 55 2,344.7
Lingcod................................... S of 40'10[deg] N lat....... 857.7 45 386.0 55 471.7
Longnose skate \a\........................ Coastwide................... 1,851.7 90 1,666.5 10 185.2
Longspine thornyhead...................... N of 34[deg]27' N lat....... 2,419.6 95 2,298.6 5 121.0
Pacific cod............................... Coastwide................... 1,093.8 95 1,039.1 5 54.7
Pacific whiting \d\....................... Coastwide................... 348,968 100 348,968 0 0
Pacific ocean perch \e\................... N of 40[deg]10' N lat....... 4,206.6 95 3,996.3 5 210.3
[[Page 21384]]
Petrale sole.............................. Coastwide................... 2,524.4 95 2,398.2 5 126.2
---------------------------------------------------------------
Sablefish................................. N of 36[deg] N lat.......... NA See Table 2c
---------------------------------------------------------------
Sablefish................................. S of 36[deg] N lat.......... 2,027.8 42 851.7 58 1,176.1
Shortspine thornyhead..................... N of 34[deg]27' N lat....... 1,603.7 95 1,523.5 5 80.2
Shortspine thornyhead..................... S of 34[deg]27' N lat....... 881.8 NA 50.0 NA 831.8
Splitnose rockfish........................ S of 40[deg]10' N lat....... 1,714.4 95 1,628.7 5 85.7
Starry flounder........................... Coastwide................... 433.2 50 216.6 50 216.6
Widow rockfish \f\........................ Coastwide................... 10,950.6 91 9,965.0 9 985.6
YELLOWEYE ROCKFISH........................ Coastwide................... 42.9 8 3.4 92 39.5
Yellowtail rockfish....................... N of 40[deg]10' N lat....... 4,940.9 88 4,348.0 12 592.9
Minor Shelf Rockfish North................ N of 40[deg]10' N lat....... 1,971.1 60.2 1,186.6 39.8 784.5
Minor Shelf Rockfish South................ S of 40[deg]10' N lat....... 1,545.9 12.2 188.6 87.8 1,357.3
Minor Slope Rockfish North................ N of 40[deg]10' N lat....... 1,651.2 81 1,337.5 19 313.7
Minor Slope Rockfish South................ S of 40[deg]10' N lat....... 722.8 63 455.4 37 267.4
Other Flatfish............................ Coastwide................... 5,791.5 90 5,212.4 10 579.2
--------------------------------------------------------------------------------------------------------------------------------------------------------
\a\ Allocations decided through the biennial specification process.
\b\ 46 mt of the total trawl allocation of canary rockfish is allocated to the MS and C/P sectors, as follows: 30 mt for the MS sector, and 16 mt for
the C/P sector.
\c\ Consistent with regulations at Sec. 660.55(c), 9 percent (66.8 mt) of the total trawl allocation for darkblotched rockfish is allocated to the
Pacific whiting fishery, as follows: 28.1 mt for the Shorebased IFQ Program, 16.0 mt for the MS sector, and 22.7 mt for the C/P sector. The tonnage
calculated here for the Pacific whiting IFQ fishery contributes to the total shorebased trawl allocation, which is found at Sec.
660.140(d)(1)(ii)(D).
\d\ Consistent with regulations at Sec. 660.55(i)(2), the commercial harvest guideline for Pacific whiting is allocated as follows: 34 percent
(118,649 mt) for the C/P Coop Program; 24 percent (83,752 mt) for the MS Coop Program; and 42 percent (146,567 mt) for the Shorebased IFQ Program. No
more than 5 percent of the Shorebased IFQ Program allocation (7,328 mt) may be taken and retained south of 42[deg] N lat. before the start of the
primary Pacific whiting season north of 42[deg] N lat.
\e\ Consistent with regulations at Sec. 660.55(c), 17 percent (679.4 mt) of the total trawl allocation for Pacific ocean perch is allocated to the
Pacific whiting fishery, as follows: 285.3 mt for the Shorebased IFQ Program, 163.0 mt for the MS sector, and 231.0 mt for the C/P sector. The tonnage
calculated here for the Pacific whiting IFQ fishery contributes to the total shorebased trawl allocation, which is found at Sec.
660.140(d)(1)(ii)(D).
\f\ Consistent with regulations at Sec. 660.55(c), 10 percent (996.5 mt) of the total trawl allocation for widow rockfish is allocated to the whiting
fisheries, as follows: 418.5 mt for the shorebased IFQ fishery, 239.2 mt for the mothership fishery, and 338.8 mt for the catcher/processor fishery.
The tonnage calculated here for the whiting portion of the shorebased IFQ fishery contributes to the total shorebased trawl allocation, which is found
at Sec. 660.140(d)(1)(ii)(D).
0
5. In Sec. 660.140, revise paragraph (d)(1)(ii)(D) to read as follows:
Sec. 660.140 Shorebased IFQ Program.
* * * * *
(d) * * *
(1) * * *
(ii) * * *
(D) Pacific whiting and non-whiting QP shorebased trawl
allocations. For the trawl fishery, NMFS will issue QP based on the
following shorebased trawl allocations:
Table 1 to Paragraph (d)(1)(ii)(D)
----------------------------------------------------------------------------------------------------------------
2019 2020
Shorebased Shorebased
IFQ species Area trawl trawl
allocation allocation
(mt) (mt)
----------------------------------------------------------------------------------------------------------------
Arrowtooth flounder........................ Coastwide.......................... 12,735.1 10,052.3
Bocaccio................................... South of 40[deg]10' N lat.......... 800.7 767.1
Canary rockfish............................ Coastwide.......................... 953.6 894.3
Chilipepper................................ South of 40[deg]10' N lat.......... 1,838.3 1,743.8
COWCOD..................................... South of 40[deg]10' N lat.......... 2.2 3.2
Darkblotched rockfish...................... Coastwide.......................... 658.4 703.4
Dover sole................................. Coastwide.......................... 45,979.2 45,979.2
English sole............................... Coastwide.......................... 9,375.1 9,417.9
Lingcod.................................... North of 40[deg]10' N lat.......... 2,051.9 1,903.4
Lingcod.................................... South of 40[deg]10' N lat.......... 462.5 386.0
Longspine thornyhead....................... North of 34[deg]27' N lat.......... 2,420.0 2,293.6
Minor Shelf Rockfish complex............... North of 40[deg]10' N lat.......... 1,155.2 1,151.6
Minor Shelf Rockfish complex............... South of 40[deg]10' N lat.......... 188.6 188.6
Minor Slope Rockfish complex............... North of 40[deg]10' N lat.......... 1,248.8 1,237.5
Minor Slope Rockfish complex............... South of 40[deg]10' N lat.......... 456.0 455.4
Other Flatfish complex..................... Coastwide.......................... 5,603.7 5,192.4
Pacific cod................................ Coastwide.......................... 1,034.1 1,034.1
Pacific ocean perch........................ North of 40[deg]10' N lat.......... 3,697.3 3,602.2
Pacific whiting............................ Coastwide.......................... 152,326.5 146,567
Petrale sole............................... Coastwide.......................... 2,453.0 2,393.2
Sablefish.................................. North of 36[deg] N lat............. 2,581.3 2,636.8
[[Page 21385]]
Sablefish.................................. South of 36[deg] N lat............. 834.0 851.7
Shortspine thornyhead...................... North of 34[deg]27' N lat.......... 1,506.8 1,493.5
Shortspine thornyhead...................... South of 34[deg]27' N lat.......... 50.0 50.0
Splitnose rockfish......................... South of 40[deg]10' N lat.......... 1,646.7 1,628.7
Starry flounder............................ Coastwide.......................... 211.6 211.6
Widow rockfish............................. Coastwide.......................... 9,928.8 9,387.1
YELLOWEYE ROCKFISH......................... Coastwide.......................... 3.4 3.4
Yellowtail rockfish........................ North of 40[deg]10' N lat.......... 4,305.8 4,048.0
----------------------------------------------------------------------------------------------------------------
* * * * *
[FR Doc. 2020-08019 Filed 4-16-20; 8:45 am]
BILLING CODE 3510-22-P