Magnuson-Stevens Act Provisions; Fisheries Off West Coast States; Pacific Coast Groundfish Fishery; Pacific Coast Groundfish Fishery Management Plan; Amendment 29; 2021-22 Biennial Specifications and Management Measures, 62492-62537 [2020-21783]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 660
[Docket No. 200928–0257]
RIN 0648–BJ74
Magnuson-Stevens Act Provisions;
Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery;
Pacific Coast Groundfish Fishery
Management Plan; Amendment 29;
2021–22 Biennial Specifications and
Management Measures
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule; request for
comments.
AGENCY:
This proposed rule would
establish the 2021–22 harvest
specifications for groundfish 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 and
the Pacific Coast Groundfish Fishery
Management Plan (PCGFMP). This
proposed rule would also revise the
management measures that are intended
to keep the total annual catch of each
groundfish stock or stock complex
within the annual catch limits. These
proposed measures are intended to help
prevent overfishing, rebuild overfished
stocks, achieve optimum yield, and
ensure that management measures are
based on the best scientific information
available. Additionally, this proposed
rule announces the receipt of exempted
fishing permit applications. NMFS has
made a preliminary determination that
these applications warrant further
consideration. NMFS requests public
comment on these applications. This
action also would implement
Amendment 29 to the PCGFMP, which
would designate shortbelly rockfish as
an ecosystem component species, and
would make changes to the trawl/nontrawl allocations for blackgill rockfish
within the southern slope complex
south of 40°10′ North latitude (N lat.),
petrale sole, lingcod south of 40°10′ N
lat., and widow rockfish.
DATES: Comments must be received no
later than November 2, 2020.
ADDRESSES: Submit your comments,
identified by NOAA–NMFS–2020–0098,
by either of the following methods:
• Federal e-Rulemaking Portal: Go to
www.regulations.gov/
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SUMMARY:
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#!docketDetail;D=NOAA-NMFS-20200098, click the ‘‘Comment Now!’’ icon,
complete the required fields, and enter
or attach your comments. The exempted
fishing permit (EFP) applications will be
available under Supporting Documents
through the same link.
• Mail: Submit written comments to
Barry Thom, Regional Administrator,
West Coast Region, NMFS, 7600 Sand
Point Way NE, Seattle, WA 98115–0070.
Instructions: NMFS may not consider
comments if they are sent by any other
method, to any other address or
individual, or received after the
comment period ends. All comments
received are a part of the public record
and NMFS will post 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 is publicly
accessible. NMFS will accept
anonymous comments (enter ‘‘N/A’’ in
the required fields if you wish to remain
anonymous).
Electronic Access
This 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 West
Coast Region website at https://
www.westcoast.fisheries.noaa.gov/
fisheries/groundfish/ and at
the Pacific Fishery Management
Council’s website at https://
www.pcouncil.org. The final 2020 Stock
Assessment and Fishery Evaluation
(SAFE) report for Pacific Coast
groundfish, as well as the SAFE reports
for previous years, are available from
the Pacific Fishery Management
Council’s website at https://
www.pcouncil.org.
FOR FURTHER INFORMATION CONTACT:
Karen Palmigiano, phone: 206–526–
4491 or email: karen.palmigiano@
noaa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
Chapter 5 of the Pacific Coast
Groundfish Fishery Management Plan
(PCGFMP) requires the Pacific Fishery
Management Council (Council) to assess
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the biological, social, and economic
conditions of the Pacific coast
groundfish fishery and use this
information to develop harvest
specifications and management
measures at least biennially. This
proposed rule is based on the Council’s
final recommendations for harvest
specifications and management
measures for the 2021–22 biennium
made at its April and June 2020
meetings.
The Council deemed the proposed
regulations necessary and appropriate to
implement these actions in an August,
26, 2020, letter from Council Executive
Director, Chuck Tracy, to Regional
Administrator Barry Thom. Under the
Magnuson-Stevens Fishery
Conservation and Management Act
(Magnuson-Stevens Act), NMFS is
required to publish proposed rules for
comment after preliminarily
determining whether they are consistent
with applicable law. We are seeking
comment on the proposed regulations in
this action and whether they are
consistent with the PCGFMP, the
Magnuson-Stevens Act and its National
Standards, and other applicable law.
Concurrent with this proposed rule,
NMFS also published a Notice of
Availability (NOA) to announce the
proposed Amendment 29 to the
PCGFMP. The NOA requests public
review and comment on proposed
changes to the Council fishery
management plan document (85 FR
54529; September 2, 2020).
A. Specification and Management
Measure Development Process
The Northwest Fisheries Science
Center (NWFSC) conducted full stock
assessments in 2019 for 7 of the 128
stocks 1 currently included under the
PCGFMP as stocks that require
conservation and management (cabezon,
big skate, longnose skate, sablefish,
cowcod, gopher rockfish, and black-andyellow rockfish). Additionally, the
NWFSC reviewed assessment updates
for Petrale sole and widow rockfish, as
well as catch-only assessment updates
for a number of previously assessed
stocks (black rockfish, blackgill rockfish,
California blue/deacon rockfish north of
Point Conception, canary rockfish,
China rockfish, darkblotched rockfish,
Dover sole, lingcod, longspine
thornyheads, rougheye and blackspotted
rockfishes, and shortspine thornyhead).
The NWFSC did not update assessments
for the remaining stocks, so harvest
1 Stocks for which annual catch limits (ACLs) or
ACL contributions to stock complex ACLs are
calculated. Assessments do not include stocks
designated as ecosystem component species.
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specifications for these stocks are based
on assessments from previous years.
The full stock assessments used to set
catch limits for this biennium are
available on the Council website
(https://www.pcouncil.org/).
The Council’s stock assessment
review panel (STAR panel) reviewed the
stock assessments, including
assessments on stocks for which some
biological indicators are available, as
described below, for technical merit,
and to determine that each stock
assessment document was sufficiently
complete. Finally, the Council’s
Scientific and Statistical Committee
(SSC) reviewed the stock assessments
and STAR panel reports and made its
recommendations to the Council
(Agenda Item H.5, September 2019
Council Meeting).
The Council considered the new stock
assessments, stock assessment updates,
catch-only updates, public comment,
recommendations from the SSC, and
advice from its advisory bodies over the
course of six Council meetings during
development of its recommendations for
the 2021–22 harvest specifications and
management measures. At each Council
meeting between June 2019 and June
2020, the Council made a series of
decisions and recommendations that
were, in some cases, refined after further
analysis and discussion. Table 2 in the
Analysis describes the Council’s
meeting schedule for developing the
2021–22 biennial harvest specifications.
Additionally, detailed information,
including the supporting documentation
the Council considered at each meeting,
is available at the Council’s website,
www.pcouncil.org.
The 2021–22 biennial management
cycle was the third cycle following
PCGFMP Amendment 24 (80 FR 12567,
March 10, 2015), which established
default harvest control rules and was
analyzed through an Environmental
Impact Statement (EIS) (Final
Environmental Impact Statement for
Pacific Coast Groundfish Harvest
Specifications and Management
Measures for 2015–2016 and Biennial
Periods Thereafter, and Amendment 24
to the PCGFMP, published January
2015). The EIS described the ongoing
implementation of the PCGFMP and
default harvest control rules, along with
10-year projections for harvest
specifications and a range of
management measures. Under
Amendment 24, the default harvest
control rules used to determine the
previous biennium’s harvest
specifications (i.e., overfishing limits
[OFLs], acceptable biological catches
(ABCs), and annual catch limits [ACLs])
are applied automatically to the best
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scientific information available to
determine the future biennium’s harvest
specifications. NMFS implements
harvest specifications based on the
default harvest control rules used in the
previous biennium unless the Council
makes a recommendation to deviate
from the default. Therefore, this rule
implements the default harvest control
rules, consistent with the last biennium
(2019–20), for most stocks, and
discusses Council-recommended
departures from the defaults. The
Analysis supporting this action
identifies the preferred harvest control
rules, management measures, and other
management changes that were not
described in the 2015 EIS, and will be
posted on the NMFS West Coast Region
web page (see Electronic Access).
Information regarding the OFLs,
ABCs, and ACLs proposed for
groundfish stocks and stock complexes
in 2021–22 is presented below, followed
by a discussion of the proposed
management measures for commercial
and recreational groundfish fisheries.
II. Proposed Harvest Specifications
This proposed rule would set 2021–22
harvest specifications and management
measures for 127 of the 128 groundfish
stocks which currently have ACLs or
ACL contributions to stock complexes
managed under the PCGFMP, except for
Pacific whiting. Pacific whiting harvest
specifications are established annually
through a separate bilateral process with
Canada. Shortbelly rockfish, which is
currently managed with harvest
specifications, would no longer be
managed with harvest specifications
beginning in the 2021–22 biennium and
would instead be classified as an
ecosystem component species. The
change to shortbelly management is
made through Amendment 29 to the
PCGFMP and is discussed in detail in
the NOA for that amendment. Public
comment is open on the NOA (see
ADDRESSES).
The proposed OFLs, ABCs, and ACLs
are based on the best available
biological and socioeconomic data,
including projected biomass trends,
information on assumed distribution of
stock biomass, and revised technical
methods used to calculate stock
biomass. The PCGFMP specifies a series
of three stock categories for the purpose
of setting maximum sustainable yield
(MSY) 2, OFLs, ABCs, ACLs, and
rebuilding standards. Category one
represents the highest level of
information quality available, while
2 MSY is the largest long-term average catch that
can be taken from a fish stock under prevailing
environmental and fishery conditions.
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category three represents the lowest.
Category one stocks are the relatively
few stocks for which the NWFSC can
conduct a ‘‘data rich’’ quantitative stock
assessment that incorporates catch-atage, catch-at-length, or other data. The
SSC can generally calculate OFLs and
overfished/rebuilding thresholds for
these stocks, as well as ABCs, based on
the uncertainty of the biomass estimated
within an assessment or the variance in
biomass estimates between assessments
for all stocks in this category. The set of
category two stocks includes a large
number of stocks for which some
biological indicators are available, yet
status is based on a ‘‘data-moderate’’
quantitative stock assessment. The
category three stocks include minor
stocks which are caught, but for which
there is, at best, only information on
landed biomass. For stocks in this
category, there is limited data available
for the SSC to quantitatively determine
MSY, OFL, or an overfished threshold.
Typically, catch-based methods (e.g.,
depletion-based stock reduction
analysis, depletion corrected average
catch, and average catches) are used to
determine the OFL for category three
stocks. A detailed description of each of
these categories can be found in Section
4.2 of the PCGFMP.
A. Proposed OFLs for 2021 and 2022
The OFL serves as the maximum
amount of fish that can be caught in a
year without resulting in overfishing.
Overfishing occurs when a stock has a
harvest rate, denoted as Fx%, is set
higher than the rate that produces the
stock’s MSY. The SSC derives OFLs for
groundfish stocks with stock
assessments by applying the harvest rate
to the current estimated biomass (B).
Harvest rates represent the rates of
fishing mortality (F) that will reduce the
female spawning potential ratio (SPR) to
X percent of its unfished level. As an
example, a harvest rate of F40% is more
aggressive than F45% or F50% harvest
rates because F40% allows more fishing
mortality on a stock (as it allows a
harvest rate that would reduce the stock
to 40 percent of its unfished level). The
OFL does not account for scientific or
management uncertainty, so the SSC
typically recommends an ABC that is
lower than the OFL in order to account
for this uncertainty. Usually, the greater
the amount of scientific uncertainty, the
lower the ABC is set compared to the
OFL.
For 2021–22, the Council maintained
its policy of using a default harvest rate
as a proxy for the fishing mortality rate
that is expected to achieve FMSY. The
Council also maintained the same
default harvest rate proxies as used in
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the 2019–20 biennium, based on the
SSC’s recommendations: F30% for
flatfish (meaning an SRP harvest rate
that would reduce the stock to 30
percent of its unfished level), F50% for
rockfish (including longspine and
shortspine thornyheads), F50% for
elasmobranchs, and F45%for other
groundfish such as sablefish and
lingcod. For unassessed stocks, the
Council recommended using a historical
catch-based approach (e.g., average
catch, depletion-corrected average
catch, or depletion-based stock
reduction analysis) to set the OFL. See
Tables 1a and 2a to Part 660, Subpart C
in the proposed regulatory text
supporting this rule for the proposed
2021–22 OFLs.
A detailed description of the scientific
basis for all of the SSC-recommended
OFLs proposed in this rule is included
in the SAFE document for 2020,
available at the Council’s website,
www.pcouncil.org.
B. Proposed ABCs for 2021 and 2022
The ABC is the stock or stock
complex’s OFL reduced by an amount
associated with scientific uncertainty.
The SSC-recommended P star-sigma
approach determines the amount by
which the OFL is reduced to account for
this uncertainty. Under this approach,
the SSC recommends a sigma (s) value.
The s value is generally based on the
scientific uncertainty in the biomass
estimates generated from stock
assessments and is usually related to the
stock category. After the SSC determines
the appropriate s value, the Council
chooses a P star (P*) based on its chosen
level of risk aversion considering the
scientific uncertainties. A P* of 0.5
equates to no additional reduction for
scientific uncertainty beyond the s
value reduction. The PCGFMP specifies
that the upper limit of P* will be 0.45.
The P*-sigma approach is discussed in
detail in the proposed and final rules for
the 2011–12 (75 FR 67810, November 3,
2010; 76 FR 27508, May 11, 2011) and
2013–14 (77 FR 67974, November 12,
2012; 78 FR 580, January 3, 2013)
biennial harvest specifications and
management measures.
The SSC recently endorsed new s
values that increase the scientific
uncertainty estimate and reduce the
proposed ABCs and ACLs relative to
what they could have been under the s
and P* values used in the previous
biennium. The new s values, endorsed
by the Council at its March 2019
meeting, include a new base reduction
for Category 1 stocks of 0.5 and an
increase in the buffer between the OFL
and ABC as the age of the assessment
increases. Currently, s is the same for
each year regardless of the age of the
assessment. Table 1 provides the s
values used in previous biennium and
the new s values with a higher base year
deduction and progressively increasing
s values with the age of the assessment.
Based on the new methodology, the
SSC quantified major sources of
scientific uncertainty in the estimates of
OFLs and generally recommended a s
value of 0.5 for category one stocks
(previously 0.36), a s value of 1.0 for
category two stocks (previously 0.72),
and a s value of 2.0 for category three
stocks (previously 1.44). For category
two and three stocks, there is greater
scientific uncertainty in the OFL
estimate because the assessments for
these stocks are informed by less data
than the assessments for category one
stocks. Therefore, the scientific
uncertainty buffer is generally greater
than that recommended for stocks with
data-rich stock assessments. Assuming
the same P* is applied, a larger s value
results in a larger reduction from the
OFL. For 2021–22, the Council
continued the general policy of using
the SSC-recommended s values for each
stock category.
For 2021–22, the Council maintained
the P* policies it established for the
previous biennium for most stocks,
except Oregon black rockfish, cowcod
south of 40°10′ N lat., sablefish, and
shortbelly rockfish. The Council
considered alternative P* values for
Petrale sole but ultimately decided to
stay with the default P* value used in
the previous biennium. As was done in
2015–16, 2017–18, and 2019–20, the
Council recommended using P* values
of 0.45 for all individually managed
category one stocks, except sablefish
and yelloweye rockfish. Combining the
category one s value of 0.5 with the P*
value of 0.45 results in a reduction of
6.1 percent from the OFL when deriving
the ABC. For category two stocks, the
Council’s general policy was to apply a
P* of 0.4, with a few exceptions. The
Council recommended applying a P* of
0.45 for big skate, cowcod south of
34°27′ N lat., English sole, longnose
skate, Pacific ocean perch, and all of the
stocks managed in the Oregon blue/
deacon/black rockfish complex,
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Nearshore Rockfish complexes, and the
Other Fish complex. When combined
with the s values of 1.00 for category
two, a P* value of 0.45 corresponds to
an 11.8 percent reduction and a P*
value of 0.40 corresponds to a 22.4
percent reduction. For category three
stocks, the Council’s general policy was
to apply a P* value of 0.45 for these
stocks, except the Council
recommended a P* value of 0.40 for
cowcod between 40°10′ N lat. and
34°27′ N lat., Pacific cod, starry
flounder, and all stocks in the Other
Flatfish complex. When combined with
the s values of 2.00 for category three,
a P* value of 0.45 corresponds to 22.2
percent reduction and a P* value of 0.40
corresponds to a 39.8 percent reduction.
See Tables 1–3 in Agenda Item H.8,
Supplemental Attachment 2, September
2019 Council meeting for the full
description of s and P* values by stock.
See Tables 1a and 2a to Part 660,
Subpart C in the in the proposed
regulatory text of this proposed rule for
the proposed 2021–22 ABCs.
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C. Proposed ACLs for 2019 and 2020
The Council recommends ACLs for
each stock and stock complex that is in
need of conservation and management
or ‘‘in the fishery,’’ as defined in the
PCGFMP. To determine the ACL for
each stock, the Council will determine
the best estimate of current stock
abundance and its relation to the
precautionary and overfished/rebuilding
thresholds. Under the PCGFMP, the
biomass level that produces MSY, or
BMSY, is defined as the precautionary
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threshold. When the biomass for an
assessed category one or two stock falls
below BMSY, the ACL is set below the
ABC using a harvest rate reduction to
help the stock return to the BMSY level,
which is the management target for
groundfish stocks. If a stock biomass is
larger than BMSY, the ACL may be set
equal to the ABC, or the ACL may be set
below the ABC to address conservation
objectives, socioeconomic concerns,
management uncertainty, or other
factors necessary to meet management
objectives. The overfished/rebuilding
threshold is 25 percent of the estimated
unfished biomass level for non-flatfish
stocks or 50 percent of BMSY, if known.
The overfishing/rebuilding threshold for
flatfish stocks is 12.5 percent of the
estimated unfished biomass level. When
a stock is below BMSY (the precautionary
threshold) but above the overfishing/
rebuilding threshold, it is considered to
be in the precautionary zone.
Under PCGFMP Amendment 24, the
Council set up default harvest control
rules, which established default policies
that would be applied to the best
available scientific information to set
ACLs each biennial cycle, unless the
Council has reasons to diverge from that
harvest control rule. A complete
description of the default harvest
control rules for setting ACLs is
described in the proposed and final rule
for the 2015–16 harvest specifications
and management measures and
PCGFMP Amendment 24 (80 FR 687,
January 6, 2015; 80 FR 12567, March 10,
2015).
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The PCGFMP defines the 40–10
harvest control rule for stocks with a
BMSY proxy of B40% that are in the
precautionary zone as the standard
reduction. The analogous harvest
control rule with the standard reduction
for assessed flatfish stocks is the 25–5
harvest control rule for flatfish stocks
with a BMSY proxy of B25%. The further
the stock biomass is below the
precautionary threshold, the greater the
reduction in ACL relative to the ABC,
until at B10% for a stock with a BMSY
proxy of B40%, or B5% for a stock with
a BMSY proxy of B25%, the ACL would
be set at zero.
Under the PCGFMP, the Council may
recommend setting the ACL at a
different level than what the default
harvest control rules specify as long as
the ACL does not exceed the ABC and
complies with the requirements of the
Magnuson-Stevens Act (see Chapter 8 of
the analysis for information on the
Magnuson-Stevens Act and other
applicable laws). For most of the stocks
and all the stock complexes managed
with harvest specifications for 2021–22,
the Council chose to maintain the
default harvest control rules from the
previous biennial cycle. For four stocks,
Oregon Black rockfish, cowcod south of
40°10′ N lat., sablefish, and shortbelly
rockfish, the Council recommended
deviating from the default harvest
control rule. Table 2 presents a
summary table of the proposed changes
to default harvest control rules for
certain stocks for 2021–22. Each of these
changes is discussed further below.
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Cowcod South of 40°10′ N Lat.
A new cowcod assessment conducted
by the NWFSC in 2019 indicated the
stock south of 40°10′ N lat. had
transitioned from a rebuilding stock to
a stock with current depletion estimate
at the start of 2019 of 57 percent of
unfished spawning output (Agenda Item
H.5. Attachment 9, September 2019),
which is far above the precautionary
threshold of 50 percent. When a stock
is determined to be rebuilt, its harvest
control rule automatically reverts back
to the default harvest control rule for the
next biennium. For the 2021–22
biennium, cowcod south of 40°10′ N lat.
was the only stock declared rebuilt.
Consistent with the Council’s
preferred alternative, this action
proposes that the cowcod south of
40°10′ N lat. ACL would be set equal to
the ABC with a P* of 0.4, resulting in
ACLs of 84 mt in 2021 and 82 mt in
2022. The Council recommended a
lower P* value for cowcod south of
40°10′ N lat. than what would have been
applied under the default P* value (P*
= 0.45) to address the relatively high
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uncertainty in the estimated biomass
and productivity in the cowcod
assessment due to a lack of adequate
data (particularly age data) for
estimating growth, natural mortality,
and recruitment. The revised P* value
of 0.40 is consistent with other category
two stocks. See Section 2.2.2.2 of the
Analysis for more information on the
Council’s consideration of alternative
harvest specifications for cowcod south
of 40°10′ N lat.
The resulting ACLs would increase by
more than eight times the amount in
place in 2019 (10 mt). As an additional
precaution due to the uncertainty in the
assessment, the Council also
recommended, and NMFS is proposing,
an ACT of 50 mt for cowcod south of
40°10′ N lat. The ACT is a management
measure and is discussed further in
Section III of this preamble.
Oregon Black Rockfish
Oregon black rockfish is a category
two stock, managed as part of the
Oregon blue/deacon/black rockfish
complex. Oregon black rockfish was
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first assessed as a single stock in 2015.
In 2019, the Oregon black rockfish stock
was estimated to be at 56 percent of its
unfished spawning output. For 2021–22,
the NWFSC conducted a catch-only
update to the 2015 assessment by
adding realized catch data from 2015–
2018 and estimates of catch for 2019
and 2020. In Oregon, realized catches
were closer to projected catches in
2015–2017, but lower in 2018 resulting
in OFL projections for 2021 and 2022
that are slightly higher than the
projections in the previous assessment.
In addition to the catch data update, the
SSC applied the newly endorsed s
values to each year in the forecast (as
discussed above in B. Proposed ABCs
for 2021 and 2022). Because Oregon
black rockfish is a category two stock, a
base s value of 1.0 was applied to years
2021–2030 (Table 1–2 in Agenda Item
H.5, Attachment 15, September 2019).
Black rockfish was last assessed in 2015,
so the stock is also subject to further s
value reductions. However, the Council
recommended and NMFS is proposing a
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phased-in approach to incorporating
this additional ABC reduction.
Black rockfish is the primary target for
the Oregon recreational and commercial
nearshore fisheries. In 2017, Oregon
recreational fisheries were shut down
early because of black rockfish
concerns, and the Council received
public testimony as to the severe
negative consequences for charter
business operators and tourist-revenue
dependent coastal communities
resulting from this closure. Due to the
constraining nature of black rockfish in
Oregon and the biomass level being
above the precautionary threshold, the
Oregon Department of Fish and Wildlife
(ODFW) requested the Council consider
an alternative for the 2021–22 biennium
where the 2020 ABC (512 mt) is
specified for 2021 and 2022, and the
ACLs are set equal to ABCs. The
Magnuson-Stevens Act and the
PCGFMP allow the SSC to recommend
an ABC that differs from the ABC
control rule on a case by case basis,
provided the SSC offers justification for
its recommended deviation. In 2023, the
current default harvest control rule
(ABC = ACL, P* of 0.45) would once
again apply to Oregon black rockfish. In
this case, long-term projections under
the Council’s default harvest control
rule and the alternative 2021 and 2022
ABC both result in a projected stock
biomass at 54 percent of its unfished
spawning output in 2030. Stocks with
biomass estimates greater than 40
percent depletion are above the
precautionary thresholds in the
PCGFMP. Because the biomass is the
same under either option, the SSC
recommended the alternative 2021 and
2022 ABC.
Therefore based on the Analysis, the
Council has recommended and NMFS is
proposing alternative harvest
specifications for Oregon black rockfish
as part of the Oregon blue/deacon/black
rockfish complex. The alternative
harvest control rule would implement
an ACL for the 2021 and 2022 biennium
of 512 mt in each year. This ACL
contributes to the overall stock complex
ACL.
Sablefish
The NWFSC completed a full stock
assessment for sablefish in 2019
(Agenda Item H.5. Attachment 7,
September 2019). In 2019, the sablefish
stock is estimated to be at 39 percent of
unfished spawning output. However,
biomass is projected to increase, and the
spawning output is projected to be
above the precautionary threshold (B40)
in 2021. The expected increase in
biomass is driven in part by the
estimated, but highly uncertain, size of
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the 2016 year class. Now that sablefish
biomass is projected to be above BMSY,
the Council considered alternative
harvest specifications for the 2021–22
biennium.
Additionally, the Council
recommended revising the
apportionment of the ACL north and
south 36° N Lat. Each biennium, the
coastwide sablefish ABC is apportioned
to ACLs for the areas north and south
of 36° N Lat. based on a percentage. In
2019–20, the Council used the average
swept area biomass from the trawl
survey to determine this percentage.
However, for the 2021–22 biennium, the
Council recommended updating its
methods for determining this percentage
and will now be using a rolling 5-year
average of the swept area biomass
instead of the long-term average. This
results in an increase in the percentage
of the sablefish apportioned north of 36°
N Lat. ACL from 73.7 percent to 78.4
percent and a decrease in the percentage
of the sablefish apportioned south of 36°
N Lat. ACL from 26.3 percent to 21.5
percent. The change in apportionment
of the north and south sablefish ACLs is
expected to result in higher attainment
of both of the ACLs and should better
align with recent catches by area.
Under the default harvest control rule,
the ABC would be set equal to the ACL
with a P* value of 0.4. The P* value of
0.4 was set when the unfished spawning
output was below 40 percent. Under a
P* value of 0.4, the unfished spawning
output is estimated to be at 46 percent
in 2021 and 47 percent by 2030
assuming full ACL removals each year.
The ACLs would no longer be subject to
the 40–10 rule reduction because the
stock would be above the BMSY proxy in
2021 and would therefore be set equal
to the ABC. The ACLs under the default
harvest control rule and the revised
apportionment percentages would be
6,435 mt for north of 36° N Lat. and
1,773 mt for south of 36° N Lat. in 2021.
In 2022, the ACL would be 6,124 mt for
north of 36° N Lat. and 1,687 mt for
south of 36° N Lat.
Based on the 2019 sablefish stock
assessment, the Council recommended
an alternative harvest specifications for
sablefish using a P* value of 0.45 for the
2021–22 biennium. Under the increased
P* value, the unfished spawning output
is estimated to be at 46 percent in 2021
and 44 percent by 2030, assuming full
ACL removals each year. No reduction
to the ACL would be necessary, similar
to the default, because the stock’s
unfished spawning output is above 40
percent. Therefore, under the P* value
of 0.45, the 2021 ACLs for the north and
south would be 6,479 mt and 2,312, mt,
respectively. The 2022 ACLs for the
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north and south would be 6,172 mt and
2,203 mt, respectively.
Therefore, the Council recommended,
and NMFS is proposing, to implement
an alternative harvest control rule for
sablefish for the 2021–22 biennium. The
alternative harvest control rule would
set the ABC equal to the ACL with a P*
value of 0.45 resulting in ACLs that are
higher than under the Council’s No
Action default harvest control rule for
sablefish.
Shortbelly Rockfish
Shortbelly rockfish has been a topic of
discussion on every Council agenda
beginning in November 2018 due to
higher than anticipated bycatch in
recent years. Shortbelly rockfish is
currently a species managed within the
PCGFMP in section 3.1 of the PCGFMP
and directed fishing is allowed even
though it is not the target of a directed
fishery.
As part of the 2021–22 biennium, the
Council recommended and NMFS is
proposing to reclassify shortbelly
rockfish as an ecosystem component
species through Amendment 29 to the
PCGFMP. For more information on this
reclassification, see the NOA for
Amendment 29 (see ADDRESSES).
Stocks in Rebuilding Plans
When a stock has been declared
overfished, the Council must develop
and manage the stock in accordance
with a rebuilding plan. For overfished
stocks in the PCGFMP, this means that
the harvest control rule for overfished
stocks sets the ACL based on the
rebuilding plan. The proposed rules for
the 2011–12 (75 FR 67810, November 3,
2010) and 2013–14 (77 FR 67974,
November 14, 2012) harvest
specifications and management
measures contain extensive discussions
on the management approach used for
overfished stocks, which are not
repeated here. In addition, the SAFE
document posted on the Council’s
website at https://www.pcouncil.org/
groundfish/safe-documents/ contains a
detailed description of each overfished
stock, its status and management, as
well as the SSC’s approach for
rebuilding analyses. This document
provides information on cowcod south
of 40°10′ N lat., which has rebuilt since
the last biennium, and yelloweye
rockfish which is the only remaining
rebuilding stock in the PCGFMP. The
Council proposed yelloweye rockfish
ACLs for 2021 and 2022 based on the
current yelloweye rockfish rebuilding
plan, so additional details are not
repeated here. Appendix F to the
PCGFMP contains the most recent
rebuilding plan parameters, as well as a
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history of each overfished stock, and
can be found at https://
www.pcouncil.org/groundfish/
fisherymanagement-plan/.
Yelloweye rockfish was declared
overfished in 2002. The Council
adopted a rebuilding plan for the stock
in 2004, and revised the rebuilding plan
in 2011 under Amendment 16–4 to the
PCGFMP, and again during the 2019–20
biennium.
Additionally, the Council
recommended, and NMFS is proposing,
to establish annual catch targets (ACTs)
within the nontrawl allocation harvest
guideline (HG). The nontrawl sector
includes the limited entry fixed gear
(LEFG) and open access (OA) fisheries
as well as the recreational fisheries for
Washington, Oregon, and California.
The nearshore fisheries occur off of
Oregon and California and are subject to
both Federal and state HGs as well as
other state-specific management
measures. The non-nearshore fisheries
include the limited entry and Federal
open access fixed gear fleets. Tables 3
and 4 outline the proposed harvest
specifications for 2021 and 2022 for
yelloweye rockfish.
The Council recommended using
ACTs for the nontrawl sector as a
precaution. As discussed in the
Analysis, because yelloweye rockfish
catch has been restricted for many years,
it is difficult to project encounter rates.
This precautionary approach to higher
catch limits would allow more access to
target fisheries for the nontrawl sector,
while also managing for the uncertainty
and volatility in catch of this rebuilding
stock by this sector.
Under this proposed rule, nine stocks
would have higher ACLs in 2021 and
2022 than in 2019. Of the 43 stocks and
stock complexes managed with ACLs in
2020, 21 stocks have ACLs that would
decrease in 2021 from 2020 and 12
stocks have ACLs that would be close to
the amount in place in 2020 (Table 4.6
of the Analysis). Shortbelly rockfish are
proposed to be no longer be managed
with an ACL and one stock, Pacific cod,
would have the same ACLs in 2020,
2021, and 2022. Two stocks (big skate
and cowcod south of 40°10′ N lat.) have
ACLs that would increase more than
100 percent, and one stock complex,
Washington’s cabezon/kelp greenling,
has an ACL that would increase by 92.3
percent. These increases are due to new
information provided in the 2019 stock
assessments for these stocks. The ACL
for the shelf rockfish north complex
would decrease by 26.5 percent, which
is the largest ACL decrease between
2020 and 2021, followed by the ACL for
arrowtooth flounder, which would
decrease by 22.1 percent. These
decreases are due to updated projections
based on the new sigma values.
D. Summary of ACL Changes From 2019
to 2021–22
Table 5 compares the ACLs for major
stocks for 2019, 2020, and 2021–22.
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III. Proposed Management Measures
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This section describes proposed
management measures (i.e., biennial
fishery harvest guidelines and setasides) used to further allocate the ACLs
to the various components of the fishery
and control fishing. Management
measures for the commercial fishery
modify fishing behavior during the
fishing year to ensure that catch does
not exceed the ACL, and include trip
and cumulative landing limits, time/
area closures, size limits, and gear
restrictions. Management measures for
the recreational fisheries include bag
limits, size limits, gear restrictions, fish
dressing requirements, and time/area
closures.
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A. Deductions From the ACLs
Before making allocations to the
primary commercial and recreational
components of groundfish fisheries, the
Council recommends ‘‘off-the-top
deductions,’’ or deductions from the
ACLs to account for anticipated
mortality for certain types of activities:
Harvest in Pacific Coast treaty Indian
tribal fisheries; harvest in scientific
research activities; harvest in nongroundfish fisheries (incidental catch);
and harvest that occurs under EFPs.
These off-the-top deductions are
proposed for individual stocks or stock
complexes and can be found in the
footnotes to Tables 1a and 2a to part
660, subpart C. The details of the EFPs
are discuss below in Section III., J.
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B. Tribal Fisheries
The Quileute Tribe, Quinault Indian
Nation, Makah Indian Tribe, and Hoh
Indian Tribe (collectively, ‘‘the Pacific
Coast Tribes’’) implement management
measures for Tribal fisheries both
independently as sovereign
governments and cooperatively with the
management measures in the Federal
regulations. The Pacific Coast Tribes
may adjust their Tribal fishery
management measures inseason to stay
within the Tribal harvest targets and
estimated impacts to overfished stocks.
Table 6 provides the proposed Tribal
harvest targets proposed for the 2021–22
biennium.
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C. Biennial Fishery Allocations
The Council routinely recommends 2year trawl and nontrawl allocations
during the biennial specifications
process for stocks without formal
allocations (as defined in Section 6.3.2
of the PCGFMP) or stocks where the
long-term allocation is suspended
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because the stock is declared overfished.
As part of the 2021–22 biennium, the
Council also decided to revise the 2-year
allocations for canary rockfish, as well
as Petrale sole, widow rockfish, lingcod
south of 40°10′ N lat., and the slope
rockfish complex south of 40°10′ N lat.,
which were established through
Amendment 21 to the PCGFMP (75 FR
32993, June 10, 2010), to better align
these allocations with current harvest
trends. The changes to these allocations
are proposed as part of Amendment 29
to the PCGFMP (see I. Background).
The trawl and nontrawl allocations,
with the exception of sablefish north of
36° N lat., are based on the fishery
harvest guideline. The fishery harvest
guideline is the tonnage that remains
after subtracting the off-the-top
deductions described in Section III., A,
entitled ‘‘Deductions from the ACLs,’’ in
this preamble. The trawl and nontrawl
allocations and recreational harvest
guidelines are designed to accommodate
anticipated mortality in each sector as
well as variability and uncertainty in
those mortality estimates. Additional
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information on the Council’s allocation
framework and formal allocations can
be found in Section 6.3 of the PCGFMP
and § 660.55 of the Federal regulations.
Allocations described below are
detailed in the harvest specification
tables appended to 50 CFR part 660,
subpart C, in the regulatory text of this
proposed rule.
The Council’s recommended and
NMFS’ proposed allocations are shown
Tables 1b and 2b in the proposed
regulatory text for this proposed rule
and summarized below.
Big Skate
The Council recommended and
NMFS is proposing the allocations
shown in Table 7 for big skate in 2021
and 2022. These allocations are
anticipated to accommodate estimates of
mortality of big skate, by sector, in
2021–22. Allocations of big skate are
determined on a biennial basis. For
2021–22, the Council elected to
maintain the current big skate split of 95
percent to the trawl fishery and 5
percent to the non-trawl fishery
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The Pacific Coast Tribes proposed trip
limit management in Tribal fisheries for
2021–22 for several stocks, including
several rockfish stocks and stock
complexes. This rule proposes the trip
limits for Tribal fisheries as provided to
the Council at its April 2020 meeting in
Supplemental Tribal Report 1, Agenda
Item G.6.a. For rockfish stocks, Tribal
regulations will continue to require full
retention of all overfished rockfish
stocks and marketable non-overfished
rockfish stocks. The Pacific Coast Tribes
will continue to develop management
measures, including depth, area, and
time restrictions, in the directed Tribal
Pacific halibut fishery in order to
minimize incidental catch of yelloweye
rockfish.
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resulting in a trawl allocation of 1,348.7
mt and a non-trawl allocation of 71 mt
in 2021 and 2022. No further allocations
or deductions are made.
Bocaccio South of 40°10′ N Lat.
accommodate estimates of mortality of
bocaccio, by sector, in 2021–22. In each
year, the fishery harvest guideline is
split with 39 percent going to the trawl
sectors and 61 percent to the non-trawl
sectors. For the trawl sector this results
in an allocation of 663.8 mt in 2021 and
654.4 mt in 2022. The non-trawl sectors
would receive 1,036.4 mt in 2021 and
1,021.8 mt in 2022. The non-trawl
allocation is then distributed between
the commercial (nearshore and nonnearshore fisheries) and California
recreational fisheries. In 2021, the
commercial sector would receive 30.9
percent of the non-trawl allocation or
320.2 mt, and the California recreational
sector would receive 716.2 mt. In 2022,
the same percentage would remain in
place with the commercial sector
receiving 315.7 mt and the California
recreational sector receiving 706.1 mt.
fishery harvest guideline is distributed
to the trawl and non-trawl sectors with
trawl receiving 72.3 percent and nontrawl sectors receiving 27.7 percent each
year. In 2021, the trawl sector would
receive 917 mt of canary rockfish, of
which 36 mt would be deducted to
account for bycatch in the at-sea sectors,
and the remaining 881.2 mt would be
distributed to the shorebased individual
fishing quota (IFQ) sector. The nontrawl sector would receive 351.4 mt
which is distributed to the commercial
nontrawl (126.5 mt), WA recreational
(43.2 mt), OR recreational (65 mt), and
CA recreational (116.7 mt) fisheries. In
2022, the trawl sector would receive
894.6 mt of canary rockfish, of which 36
mt would be deducted to account for
bycatch in the at-sea sectors, and the
remaining 858.6 mt would be
distributed to the shorebased IFQ sector.
The non-trawl sector would receive
343.1 mt, which is distributed to the
commercial nontrawl sector (123.5 mt),
WA recreational (42.2 mt), OR
recreational (63.5 mt), and CA
recreational (113.9 mt) fisheries.
Specifications for bocaccio are
determined through the biennial
specifications process. For 2021–22, the
Council recommended and NMFS is
proposing the allocations shown in
Table 8 for bocaccio in 2021 and 2022,
which maintain the allocation structure
from the previous biennium. These
allocations are anticipated to
Canary Rockfish
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The Council recommended and
NMFS is proposing the allocations in
Table 9 for canary rockfish in 2021 and
2022, which maintain the status quo
proportions from the 2017–18
biennium, but also combine the
commercial fixed gear harvest guideline
for the nearshore and non-nearshore
fisheries. These allocations are
anticipated to accommodate estimates of
mortality of canary rockfish, by sector,
in 2021–22. For canary rockfish, the
For 2021–22, the Council
recommended and NMFS is proposing
setting a cowcod ACT below the fishery
harvest guideline at 50 mt, and having
it function as a fishery harvest guideline
similar to the ACT in the 2017–18 and
2019–20 bienniums. The ACT would be
allocated across groundfish fisheries.
Table 9 shows the trawl/nontrawl
allocations for cowcod for 2021 and
2022. NMFS anticipates the proposed
allocation structure will keep catch
below the 2021–22 cowcod ACT. The
ACT is distributed to the trawl and non-
trawl sectors, with the trawl sector
receiving 36 percent and the non-trawl
sector receiving 64 percent each year. In
2021 and 2022, the trawl sector would
receive 18 mt of cowcod. The non-trawl
sector would receive 32 mt, which is
distributed to the commercial and
recreational sectors as a 50/50 split.
Lingcod South of 40°10′ N Lat.
The Council recommended and
NMFS is proposing the trawl/nontrawl
allocations for lingcod south of 40°10′ N
lat. in Table 10. These allocations are
anticipated to accommodate estimates of
mortality of lingcod, by sector, in 2021–
22. Specifications of lingcod south of
40°10′ N lat. were established through
Amendment 21 with a trawl/non-trawl
allocation set at 45 percent to trawl and
55 percent to non-trawl. For the 2021–
22 biennium, the Council recommended
revising the fixed percentages through
Amendment 29 to the PCGFMP to better
align with current catch levels and
provide some relief to the nontrawl
sector which is usually constrained by
lingcod south of 40°10′ N lat. Therefore,
beginning with the 2021–22 biennium,
the Council recommended and NMFS is
proposing changing trawl/non-trawl
allocations of lingcod south of 40°10′ N
lat., so that 40 percent of the harvest
guideline for lingcod south of 40°10′ N
lat. is allocated to the trawl sector and
60 percent is allocated to the nontrawl
sector. In 2021, the distribution results
in 435.6 mt to the trawl sector and 653.4
mt to the non-trawl sectors. In 2022, the
distribution results in 463.6 mt to the
trawl sectors and 695.4 mt to the nontrawl sectors. No further allocations or
distributions are made. The NOA for
Amendment 29 is available for public
comment (see ADDRESSES).
Longnose Skate
percent to trawl and 10 percent to
nontrawl, reflect historical catch of
longnose skate in the two sectors. These
allocations are anticipated to
accommodate estimates of mortality of
longnose skate rockfish, by sector, in
2021–22. In 2021, the 90/10 distribution
results in 1,414.4 mt to the trawl sectors
and 157.2 mt to the non-trawl sectors.
In 2022, the distribution results in
1,358.6 mt to the trawl sectors and 151
mt to the non-trawl sectors.
and 2022 are shown in Table 12.
Specifications for the shelf rockfish
complex north of 40°10′ N lat. were
established through the biennial process
with a trawl/non-trawl allocation for the
2021–22 specifications of 60.2 percent
to trawl sectors and 39.8 percent to nontrawl sectors. In 2021, the distribution
results in 864.2 mt to the trawl sectors
and 571.4 mt to the non-trawl sectors.
In 2022, the distribution results in 827.5
mt to the trawl sectors and 547.1 mt to
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The Council recommended and
NMFS is proposing the trawl/nontrawl
allocations for longnose skate in Table
11. The allocation percentages, 90
Minor Shelf Rockfish
Allocations for Minor Shelf Rockfish
are recommended by the Council and
proposed by NMFS for each biennial
cycle. The proposed allocations for 2021
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the non-trawl sectors. Of the amount
going to the trawl sectors, 35 mt is
deducted each year from the trawl
allocation to account for bycatch in the
at-sea whiting sectors, with the
remaining 829.2 mt in 2021 and 792.49
mt in 2022 going to the shorebased IFQ
fishery. No further allocations or
distributions are made.
Specifications for the shelf rockfish
complex south of 40°10′ N lat. were
established through the biennial process
with a trawl/non-trawl allocation for the
2021–22 specifications of 12.2 percent
to trawl sectors and 87.8 percent to non-
trawl sectors. In 2021, the distribution
results in 161.7 mt to the trawl sectors
and 1,163.6 mt to the non-trawl sectors.
In 2022, the distribution results in 160.5
mt to the trawl sectors and 1,154.8 mt
to the non-trawl sectors. No further
allocations or distributes are made.
Slope Rockfish Complex
Council recommended the fixed
allocation be revised through
Amendment 29 to the PCGFMP and
made into a 2-year allocation, with
custom shares for blackgill rockfish, to
be reviewed each biennium. In 2021, the
distribution results in 556.9 mt to the
trawl sectors and 152.1 mt to the nontrawl sectors. In 2022, the distribution
results in 515.6 mt to the trawl sectors
and 142.1 mt to the non-trawl sectors.
The NOA for Amendment 29 is open for
public comment (see ADDRESSES).
non-trawl fishery. As part of the 2021–
22 biennium, the Council recommended
changing the fixed allocation to a
biennial allocation through Amendment
29 to the PCGFMP and revising the
percentages to better align with current
catch by sector. Therefore, beginning in
2021, specifications for Petrale sole will
be determined as part of the biennial
specifications process. For the 2021–22
biennium, 30 mt of Petrale sole will be
allocated to the nontrawl sector and the
remainder will go to the trawl sector
each year. This would shift around 150
and 130 mt to the shorebased IFQ sector
in 2021 and 2022, respectively, and
would not constrain the nontrawl
sector. In 2021, the distribution results
in 3,697.9 mt to the trawl sector. In
2022, the trawl sector would receive
3,242.5 mt. The NOA for Amendment
29 is open for public comment (see
ADDRESSES).
The slope rockfish complex south of
40°10′ N lat. is a fixed allocation with
a trawl/non-trawl allocation of 63
percent to trawl and 37 percent to nontrawl. For the 2021–22 biennium, the
Petrale Sole
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The Council recommended and
NMFS is proposing the trawl/nontrawl
allocations for Petrale sole in Table 14.
These allocations are anticipated to
accommodate estimates of mortality of
Petrale sole, by sector, in 2021–22.
Petrale sole has a fixed allocation with
a trawl/non-trawl allocation of the
fishery harvest guideline of 95 percent
to the trawl fishery and 5 percent to the
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Widow Rockfish
The Council recommended and
NMFS is proposing the trawl/nontrawl
allocations for Widow rockfish in Table
15. These allocations are anticipated to
accommodate estimates of mortality of
widow rockfish, by sector, in 2021–22.
Widow rockfish is an Amendment 21
species with a trawl/non-trawl
allocation of the fishery harvest
guideline of 91 percent to the trawl
fishery and 9 percent to the non-trawl
fishery. As part of the 2021–22
biennium, and through Amendment 29
to the PCGFMP, the Council
recommended making it a biennial
allocation and providing a fixed amount
to the nontrawl sector to better align
with current catch by sector. Therefore,
beginning in 2021, specifications for
widow rockfish will be determined as
part of the biennial specifications
process. For the 2021–22 biennium, 400
mt of widow rockfish will be allocated
to the nontrawl sector and the
remainder will go to the trawl sector
each year. This would shift just under
1,000 mt of widow rockfish to the
shorebased IFQ sector in 2021 and 2022,
and would not constrain the nontrawl
sector. In 2021, the distribution results
in 14,076.7 mt to the trawl sector. In
2022, the trawl sector would receive
13,139.7 mt. The NOA for Amendment
29 is open for public comment (see
ADDRESSES).
D. Corrections to Waypoints for Rockfish
Conservation Areas
For the 2021–22 biennium, the
Council recommended and NMFS is
proposing minor adjustments to the 40
fathom (fm) depth contour offshore of
San Mateo in Central California, and the
100 fm depth contours off of California
to more accurately refine the depth
contours, as well as the addition of a
100 fm line around the Channel Islands.
See Chapter 2 of the Analysis for more
details on these changes.
whiting sector with the remainder of the
trawl allocation going to the shorebased
IFQ sector. Set-asides are not managed
by NMFS or the Council except in the
case of a risk to the ACL.
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E. Limited Entry Trawl
The limited entry trawl fishery is
made up of the shorebased IFQ program,
whiting and non-whiting, and the at-sea
whiting sectors. For some stocks and
stock complexes with a trawl allocation,
an amount is first set-aside for the at-sea
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At-Sea Set Asides
For several species, the trawl
allocation is reduced by an amount setaside for the at-sea whiting sector. This
amount is designed to accommodate
catch by the at-sea whiting sector when
they are targeting Pacific whiting. The
Council considered several proposals to
generate amounts for these set-asides.
After much discussion and analysis, the
Council is recommending and NMFS is
proposing the set-asides in Table 16 for
the 2021–22 biennium.
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Rockfish Conservation Areas (RCAs)
are large area closures intended to
reduce the catch of a stock or stock
complex by restricting fishing activity at
specific depths. The boundaries for
RCAs are defined by straight lines
connecting a series of latitude and
longitude coordinates that approximate
depth contours. These sets of
coordinates, or lines, are not gear or
fishery specific, but can be used in
combination to define an area. NMFS
then implements fishing restrictions for
a specific gear and/or fishery within
each defined area.
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Incidental Trip Limits for IFQ Vessels
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For vessels fishing in the Shorebased
IFQ Program, with either groundfish
trawl gear or nontrawl gears, the
following incidentally-caught stocks are
managed with trip limits: Minor
Nearshore Rockfish north and south,
black rockfish, cabezon (46°16′ to 40°10′
N lat. and south of 40°10′ N lat.), spiny
dogfish, shortbelly rockfish, big skate,
Pacific whiting, and the Other Fish
complex. For all these stocks except big
skate, this rule proposes maintaining the
same IFQ fishery trip limits for these
stocks for the start of the 2021–22
biennium as those in place in 2019. For
big skate, the Council proposes an
unlimited trip limit to start the 2021
fishing year. Additionally, the Council
is recommending and NMFS is
proposing a trip limit for blackgill
rockfish within the southern slope
rockfish complex. The trip limit would
be unlimited to start the 2021 fishing
year. The purpose of the blackgill trip
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limit would be to allow the Council to
reduce targeting of blackgill rockfish
inseason, if needed. Trip limits for the
IFQ fishery can be found in Table 1
North and Table 1 South to part 660,
subpart D, in the regulatory text of this
proposed rule. Changes to trip limits
would be considered a routine measure
under § 660.60(c), and may be
implemented or adjusted, if determined
necessary, through inseason action.
F. LEFG and OA Nontrawl Fishery
Management measures for the LEFG
and OA nontrawl fisheries tend to be
similar because the majority of
participants in both fisheries use hookand-line gear. Management measures,
including area restrictions (e.g.,
nontrawl RCA) and trip limits in these
nontrawl fisheries, are generally
designed to allow harvest of target
stocks while keeping catch of overfished
stocks low. For the 2021–22 biennium,
the Council considered increasing trip
limits for almost all LEFG and OA
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fisheries, many of which are decades
old and do not reflect stocks rebuilding
in previous biennium and management
changes (e.g., stock complex
reorganizations). LEFG and OA trip
limits are specified in Table 2 (North),
Table 2 (South) to subpart E for LEFG
and in Table 3 (North) and Table 3
(South) to subpart F for OA in the
regulatory text of this proposed rule.
Sablefish Trip Limits
Sablefish are managed separately
north and south of 36° N lat. For the
portion of the stock north of 36° N lat.,
the Council recommended and NMFS is
proposing higher trip limits for the
LEFG and OA fisheries in 2021. For the
portion south of 36° N lat., the Council
recommended removing the daily trip
limit for the OA fishery but maintaining
the same weekly and bimonthly trip
limits as were in place in the start of
2019. The proposed sablefish trip limits
for 2021–22 are shown in Table 17.
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The Council recommended, and
NMFS is proposing higher trip limits for
LEFG and OA fisheries in 2021,
including trip limits for shortspine
thornyhead, longspine thornyhead,
widow rockfish, shelf rockfish,
shortbelly rockfish, canary rockfish,
Pacific ocean perch, yellowtail rockfish,
slope rockfish, darkblotched rockfish,
Lingcod, nearshore rockfish, black
rockfish, Other Flatfish, bocaccio south
of 40°10′ N lat., and chilipepper rockfish
(Agenda Item G.6.a., Supplemental GMT
Report 2, April 2020). These increases
in trip limits are meant to help members
of industry harvest more fish while still
keeping total mortality within the ACLs
for these stocks and stock complexes.
Further information on these trip limits
can be found in Section 4.3.5.1 of the
Analysis.
As part of the Council’s recommended
trip limits for the LEFG and OA
fisheries, the Council established an OA
trip limit for shortspine and longspine
thornyheads in the area between 40°10′
N lat. and 34°27′ N lat. As part of the
Council’s action during the 2019–20
biennium, the Council recommended
and NMFS implemented, trip limits for
OA fisheries for shortspine and
longspine thornyheads north of 40°10′
N. lat. and south of 34°27′ N lat., but
inadvertently omitted the trip limit for
the area between 40°10′ N lat. and
34°27′ N lat., leaving this area closed.
The Council is recommending, and
NMFS is proposing, implementing a 50
lb (22.7 kg) per month limit for OA
fisheries targeting shortspine and
longspine thornyheads in the area
between 40°10′ N lat. and 34°27′ N lat.
This is the same trip limit currently
proposed for OA fisheries targeting
shortspine and longspine thornyheads
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north of 40°10′ N lat. See Section 4.5.6.1
of the Analysis for more information on
this change.
Primary Sablefish Tier Limits
Some limited entry fixed gear permits
are endorsed to receive annual sablefish
quota, or tier limits. Vessels registered
with one, two, or up to three of these
permits may participate in the primary
sablefish fishery. The proposed tier
limits are as follows: In 2021, Tier 1 at
58,649 lb (26,602 kg), Tier 2 at 26,659
lb (12,092 kg), and Tier 3 at 15,234 lb
(6,910 kg). For 2022, Tier 1 at 55,858 lb
(25,337 kg), Tier 2 at 25,390 lb (11,517
kg), and Tier 3 at 14,509 lb (6,581 kg).
Yellowtail Trip Limit for the Salmon
Troll Fishery North of 40°10′ N lat.
During public comment at the
November 2019 Council meeting, there
was a request to increase the yellowtail
rockfish ratio and monthly limits in the
salmon troll fishery north of 40°10′ N
lat. The current ratio and limit are 1lb
(0.45 kg) of yelloweye rockfish for every
2 lb (0.9 kg) of salmon landed, with a
200 lb (91 kg) monthly limit. As part of
the 2017–18 biennial cycle, yellowtail
rockfish was removed from the OA
multi-stock trip limit, and a new
separate trip limit of 500 lb (227 kg) per
month was recommended by the
Council and implemented by NMFS;
however, the salmon troll yellowtail
rockfish trip limit did not reflect this
change. Agenda Item G.6., Attachment 3
(April 2019) contains a detailed analysis
of the salmon troll trip limits considered
by the Council. After consideration of
the detailed analysis, the Council
recommended and NMFS is proposing
increasing the yellowtail rockfish limit
in the salmon troll fishery north of
40°10′ N lat. from 200 lbs (91 kg) to 500
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lbs (227 kg) and removing the ratio for
yellowtail to salmon.
Removal of Other Flatfish Gear
Restriction Off California
Currently, Federal regulations in
Table 2 (South) to Part 660, Subpart E
and Table 3 (South) to Part 660, Subpart
F include a gear restriction for vessels
targeting stocks in the Other Flatfish
complex south of 42° N lat. while inside
the boundaries of the nontrawl RCA.
The gear restriction limits the number of
hooks per line, size of the hooks, and
the number and size of the weights.
Other flatfish include butter sole, curlfin
sole, Pacific sanddab, rex sole, rock sole,
and sand sole, as defined in 50 CFR
660.11. This management measure was
originally implemented in 2003 to
protect bocaccio, which was overfished
at that time and was thought to provide
protections to other overfished
groundfish stocks in following years
(e.g., Petrale sole) while still allowing an
artisanal sanddab fishery off California.
However, it was determined in
subsequent cycles that it was not
effective at preventing bycatch of
overfished species. During the 2009–10
harvest specifications cycle, this
restriction was removed from
regulations for the recreational fishery
but was kept for the commercial fishery.
Since this measure was first
implemented the stocks it was intended
to protect have all been rebuilt while the
Other Flatfish complex continues to be
under-attained. Therefore, to provide
more opportunity to target stocks in the
Other Flatfish complex, the Council
recommended and NMFS is proposing
removing the gear restrictions for the
LEFG and OA fisheries targeting stocks
in the Other Flatfish complex inside the
RCA south of 42° N lat.
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Nontrawl RCA Adjustments
Increasing the LEFG and OA trip
limits, as proposed in Section III, F.,
LEFG and OA Fishery, of this proposed
rule is one way to help increase
attainment of many currently underattained species. However, as has been
discussed under public comment at
Council meetings during development
of this action, increasing trip limits
without providing access to the areas
where those fish can be found does little
to help with attainments. Therefore, as
part of the 2021–22 biennium, the
Council recommended and NMFS is
proposing the following changes to the
Nontrawl RCA off Oregon and
Washington:
• Between 40°10′ N lat. and 46°16′ N
lat. (the Oregon-Washington border):
Open the area between the 30- and 40fm management lines to hook-and-line
gear except bottom longline and
dinglebar, as defined in the ‘‘general
definitions’’ section of the Federal
regulations at 50 CFR 660.11;
• Between 38°57.5′ N lat. and 34°27′
N lat., (Point Arena to Point
Conception): Open the area between 40
fm and 50 fm; and
• South of 34°27′ N lat.: Open the
area between 75 fm and 100 fm.
These proposals, along with the
proposed changes to recreational
conservation areas (discussed in Section
III, H., Recreational Fisheries) will
provide much needed access to these
areas for the LEFG and OA fisheries to
better attain their trip limits. Section
4.7.2 of the Analysis provides a detailed
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assessment of the impacts of these
openings. Nontrawl RCA closures can
be found in the LEFG and OA trip limits
in Table 2 (North), Table 2 (South) to
subpart E for LEFG and in Table 3
(North) and Table 3 (South) to subpart
F for OA in the proposed regulatory text
of this proposed rule.
As provided in the Analysis, the
purpose of opening these areas is to
provide LEFG and OA fisheries access
to areas where they can catch abundant
target stocks, such as bocaccio, canary
rockfish, yellowtail rockfish, and widow
rockfish. All of these stocks have been
underutilized by the LEFG and OA
fisheries since they were rebuilt due to
limited access to the areas where they
can be found. Opening these areas of the
nontrawl RCA, many of which are
currently already open to other types of
fishing (i.e., trawl or recreational fishing
with hook and line gear), along with the
increased LEFG and OA trip limits for
many of these stocks and stock
complexes will likely result in greater
attainment of the nontrawl allocations
and therefore the ACLs without
increasing the risks of exceeding these
limits.
New Management Line at 38°57.5′ N
lat.
In order to make some of the proposed
changes to the Nontrawl RCA, the
Council also recommended and NMFS
is proposing creating a new
management line at 38°57.5′ N lat.,
which is Point Arena, California. Point
Arena is already defined in Federal
regulations under the definition for
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North-South Management Areas, as a
commonly used geographic coordinate.
H. Recreational Fisheries
This section describes the recreational
fisheries management measures
proposed for 2021–22. The Council
primarily recommends depth
restrictions and groundfish conservation
areas to constrain catch within the
recreational harvest guidelines for each
stock. Washington, Oregon, and
California each proposed, and the
Council recommended, different
combinations of seasons, bag limits, area
closures, and size limits for stocks
targeted in recreational fisheries. These
measures are designed to limit catch of
overfished stocks found in the waters
adjacent to each state while allowing
target fishing opportunities in their
particular recreational fisheries. The
following sections describe the
recreational management measures
proposed in each state.
Washington
The state of Washington manages its
marine fisheries in four areas: Marine
Area 1 extends from the Oregon/
Washington border to Leadbetter Point;
Marine Area 2 extends from Leadbetter
Point to the mouth of the Queets Rivers;
Marine Area 3 extends from the Queets
River to Cape Alava; and Marine Area
4 extends from Cape Alava to the Sekiu
River. This proposed rule would adopt
the following season structure in Table
18.
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target and non-target species expected
from allowing recreational hook-andline fishing in these areas would be
minimal because the areas to be opened
are very small, particularly in
comparison to the overall area used by
Washington recreational fisheries
(Agenda Item F.1.a, Supplemental
WDFW Report 1, June 2020).
Oregon
The Council proposed that Oregon
recreational fisheries in 2021–22 would
operate under an all months all depths
season structure to start the 2021 fishing
year. The Council proposed maintaining
the 2019–20 aggregate bag limits and
size limits in Oregon recreational
fisheries for 2021–22. The proposed
limits are: Three lingcod per day, with
a minimum size of 22 in (56 cm); 25
flatfish per day, excluding Pacific
halibut; and a marine fish aggregate bag
limit of 10 fish per day, where cabezon
have a minimum size of 16 in (41 cm).
The ODFW also requested that the
Council consider allowing longleader
gear fishing and ‘‘all-depth’’ Pacific
halibut fishing on the same trip, which
had been requested by Oregon anglers
during discussion of the 2019 Pacific
halibut Catch Sharing Plan process.
Currently, combining the two trip types
is prohibited; this prohibition was
meant to limit interactions with
yelloweye rockfish.
Impacts to yelloweye rockfish or other
species of concern (e.g., Chinook and
Coho salmon) are unlikely to increase
significantly under this proposed
change as effort is not expected to
increase by much. Instead, removing the
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prohibition would allow anglers already
participating in one or the other
fisheries to have additional opportunity
while offshore. As ODFW’s analysis to
the Council shows (Agenda Item F.1.a,
June 2020), over the past 2 years that the
longleader gear fishery has been allowed
to operate, the average encounter rates
of yelloweye rockfish, Chinook salmon,
and Coho salmon has been extremely
low at around 0.02, 0.6, and 6 fish per
angler, respectively. When added to the
encounters from the traditional
bottomfish fishery, the total annual
encounters would not be much different
than the recent years’ total estimates,
and should not increase the potential for
the total groundfish salmon thresholds
to be reached or exceeded. Therefore the
Council recommended and NMFS is
proposing removing the prohibition on
combining Oregon longleader trips with
all depths halibut trips.
California
The Council manages recreational
fisheries in waters adjacent to California
in five separate management areas.
Season and area closures differ between
California management areas to limit
incidental catch of overfished stocks
while providing as much recreational
fishing opportunity as possible. The
Council’s proposed California season
structure includes additional time and
depth opportunities, which are
supported by the proposed increase to
the yelloweye rockfish ACL described in
Section C. Table 19 shows the proposed
season structure and depth limits by
management area for 2021 and 2022.
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The aggregate groundfish bag limits in
waters adjacent to Washington would
continue to be nine fish in all areas with
a sub-bag limit for cabezon (one per
day), rockfish (seven per day), and
lingcod (two per day). The flatfish limit
would increase from three fish to five
fish, and is not counted towards the
groundfish bag limit of nine but is in
addition to it. The Council
recommended these season and bag
limit changes, which allow more access
to target stocks with fewer restrictions.
Consistent with the 2019–20
biennium, the Council recommended
and NMFS is proposing to continue to
prohibit recreational fishing for
groundfish and Pacific halibut inside
the North Coast Recreational Yelloweye
Rockfish Conservation Area (YRCA), a
C-shaped closed area off the northern
Washington coast. However, the Council
recommended and NMFS is proposing
opening the South Coast Recreational
YRCA and the Westport Offshore YRCA
to recreational fishing for the 2021–22
biennium. Coordinates for YRCAs are
defined at § 660.70.
Opening the South Coast Recreational
YRCA and the Westport Offshore YRCA
would provide additional access to
healthy underutilized stocks. Originally
closed to recreational fishing in 2007 to
protect canary rockfish and yelloweye
rockfish, these closures may no longer
be needed since canary rockfish has
been rebuilt and higher harvest
guidelines were implemented for
yelloweye rockfish. As stated by the
Washington Department of Fish and
Wildlife (WDFW) in their analysis for
this proposal, the additional impacts to
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The Council recommended that size
limits would remain the same as for
2020 for all stocks. However, the
Council recommended and NMFS is
proposing to eliminate the sub-bag
limits for black rockfish, canary
rockfish, and cabezon, and establish a
sub-bag limit for vermillion rockfish of
five fish.
J. Exempted Fishing Permits
This action is authorized by the
PCGFMP and the regulations
implementing the Magnuson-Stevens
Act at 50 CFR 600.745, which state that
EFPs may be used to authorize fishing
activities that would otherwise be
prohibited.
At its June 2020 meeting, the Council
recommended that NMFS approve five
EFP applications for the 2021 fishing
year and preliminarily approve the EFP
applications for the 2022 fishing year.
The Council considered these EFP
applications concurrently with the
2021–2022 biennial harvest
specifications and management process
because expected catch under most EFP
projects is included in the catch limits
for groundfish stocks. Three of the EFP
applications are renewals, and request
to test hook-and-line gear that
selectively targets underutilized,
midwater rockfish species (e.g.,
yellowtail rockfish) while avoiding
overfished, bottom-dwelling rockfish
species (e.g., yelloweye rockfish). An
EFP is necessary for these activities
because they will all occur in the nontrawl RCA, which is closed to fishing
with non-trawl fixed gear to protect
overfished groundfish stocks. The other
two EFP applications are new, and
request to retain certain prohibited
species in order to collect fisherydependent data for potential use in
upcoming stock assessments. A
summary of each EFP application is
provided below:
• Groundfish EFP Proposal—
Yellowtail Rockfish Jig Fishing off
California: The San Francisco
Community Fishing Association
(SFCFA) and private open access
fisherman Daniel Platt submitted a
renewal application for research that
has been conducted since 2013. The
purpose of the EFP project is to
continue testing the potential for a
commercial jig gear configured to target
underutilized, midwater yellowtail and
shelf rockfish species while avoiding
the rebuilding, bottom-dwelling
yelloweye rockfish. The EFP project
would require exemptions from: (1) The
prohibition to fish inside the non-trawl
RCA with non-trawl gear (see
§ 660.330(d)(12)(i)); (2) the prohibition
on transiting through the non-trawl RCA
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without non-trawl gear stowed (see
§ 660.330(d)(12)(ii)); and (3) the
prohibition on retaining and landing
groundfish harvested from inside the
non-trawl RCA with non-trawl gear (see
§ 660.330(d)(12)(iii)). If approved,
NMFS would authorize up to seven
vessels to target midwater rockfish
inside the non-trawl RCA off the
California coast—specifically between
40° 10′ north latitude (N lat.) and Point
Conception, California, at depths
ranging from 35 to 150 fathoms (64 to
274 meters (m)).
• Groundfish EFP Proposal—
Commercial Midwater Hook-and-Line
Rockfish Fishing in the RCA off the
Oregon Coast: Scott Cook, a private
fisherman of Coos Bay, Oregon
submitted a renewal application to
continue research that has been
conducted since 2019. The purpose of
the EFP project is to test a modified,
midwater trolled longline gear
configured to target underutilized,
midwater yellowtail, widow, and canary
rockfish, while avoiding the rebuilding,
bottom-dwelling yelloweye rockfish.
The EFP project would require
exemptions from: (1) The prohibition to
fish inside the non-trawl RCA with nontrawl gear (see § 660.330(d)(12)(i)); (2)
the prohibition on transiting through the
non-trawl RCA without non-trawl gear
stowed (see § 660.330(d)(12)(ii)); and (3)
the prohibition on retaining and landing
groundfish harvested from inside the
non-trawl RCA with non-trawl gear (see
§ 660.330(d)(12)(iii)). If approved,
NMFS would authorize up to five
vessels to target midwater rockfish
inside the non-trawl RCA off the Oregon
Coast—specifically in the rocky reef
habitat at depths ranging from 30 to 100
fathoms (55 to 183 m).
• Groundfish EFP Proposal—
Monterey Bay Regional EFP Chilipepper
Rockfish: Real Good Fish of Moss
Landing, California submitted a renewal
application to continue research that
has been conducted since 2019. The
purpose of the EFP project is to test a
trolled hook-and-line gear configured to
target underutilized, midwater
chilipepper rockfish and avoid the
rebuilding, bottom-dwelling yelloweye
rockfish. The EFP project would require
exemptions from: (1) The prohibition to
fish inside the non-trawl RCA with nontrawl gear (see § 660.330(d)(12)(i)); (2)
the prohibition on transiting through the
non-trawl RCA without non-trawl gear
stowed (see § 660.330(d)(12)(ii)); and (3)
the prohibition on retaining and landing
groundfish harvested from inside the
non-trawl RCA with non-trawl gear (see
§ 660.330(d)(12)(iii)). If approved,
NMFS would authorize up to 10 vessels
to target midwater rockfish inside the
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non-trawl RCA off the California coast—
specifically in areas with canyon edges
and walls that have historically
produced high volumes of chilipepper
rockfish catch and at depths ranging
from 40 to 150 fathoms (73 to 274 m).
• Groundfish EFP Proposal—
California Department of Fish and
Wildlife 2021–2022 EFP: The California
Department of Fish and Wildlife
(CDFW) submitted a new EFP
application to collect fishery-dependent
biological data for cowcod for inclusion
in future stock assessments. The EFP
project would require an exemption
from the prohibition to retain cowcod in
the California recreational fishery (see
§ 660.360(c)(3)). The EFP would also
provide that any cowcod taken and
retained would not count against the
recreational bag limit for the aggregate
of rockfish, cabezon, and greenlings. If
approved, NMFS would authorize up to
20 vessels that participate in the
California recreational fishery to retain
cowcod and transfer the cowcod to
CDFW groundfish staff upon landing.
• Groundfish EFP Proposal—
Washington Department of Fish Wildlife
Enhanced Yelloweye Recreational
Fishery Biological Sampling EFP: The
Washington Department of Fish and
Wildlife (WDFW) submitted a new EFP
application to collect fishery-dependent
biological data for yelloweye rockfish
for inclusion in future stock
assessments. The EFP project would
require an exemption from the
prohibition to retain yelloweye rockfish
in the Washington recreational fishery
(see § 660.360(c)(1)(ii)). The EFP would
also provide that any yelloweye rockfish
taken and retained would not count
against the recreational bag limit for
rockfish. If approved, NMFS would
authorize up to 10 vessels that
participate in the Washington
recreational fishery to retain yelloweye
rockfish and transfer the yelloweye
rockfish to WDFW staff upon landing.
During the 2-year period of EFP
activities from 2021 to 2022, all vessels
participating in the non-trawl RCA EFP
projects (i.e., the renewal applications
submitted by the SFCFA, Scott Cook,
and Real Good Fish) would adhere to
EFP set-asides for targeted and
incidental groundfish and other species,
which were considered and approved
by the Council at their June 2020
meeting. These EFP set-asides are offthe-top deductions from the 2021–2022
applicable ACLs, meaning any landings
and discards that occur under these
EFPs would be accounted for within the
applicable ACLs. These vessels are also
required to have 100 percent observer
coverage. All cowcod mortality under
the CDFW EFP project is expected to
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occur in conjunction with routine
recreational fishing activities and will
be calculated as part of the normal
recreational catch estimation process.
All yelloweye rockfish taken under the
WDFW EFP project would be counted
against the Washington recreational
harvest guideline for yelloweye
rockfish. NMFS would not require 100
percent observer coverage for vessels
participating in the CDFW and WDFW
EFP projects because recreational
vessels do not meet the minimum size
requirements under Federal regulations
to carry an observer.
NMFS does not expect any impacts to
the environment, essential fish habitat,
or protected or prohibited species from
these EFPs beyond those analyzed for
the groundfish fishery as a whole in
applicable biological opinions 3 4 or the
draft Environmental Assessment (EA)
for the Pacific Coast Groundfish Fishery
2021–2022 Harvest Specifications and
Management Measures.5
After publication of this document in
the Federal Register, NMFS may
approve and issue permits for the
proposed EFP projects for the 2021
fishing year after the close of the public
comment period. All five EFP
applications are available under
‘‘Supporting and Related Materials’’ (see
ADDRESSES). NMFS will consider
comments submitted in deciding
whether to approve the applications as
requested. NMFS may approve the
applications in their entirety or may
make any alterations needed to achieve
the goals of the EFP projects. NMFS
would not issue another Federal
Register notice soliciting public
comment on renewing these EFP
projects for 2022 unless: (1) The
applicants modify and resubmit their
applications to NMFS; (2) changes to
relevant fisheries regulations warrant a
revised set of exemptions authorized
under the EFP projects; or (3) NMFS’
understanding of the current biological
and economic impacts from EFP fishing
activities substantially changes.
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IV. Classification
Pursuant to section 304(b)(1)(A) of the
Magnuson-Stevens Act, the NMFS
3 Available at: https://
www.westcoast.fisheries.noaa.gov/publications/
fishery_management/groundfish/s7-groundfishbiop-121117.pdf.
4 Available at: https://www.pcouncil.org/wpcontent/uploads/2017/10/F7_Att1_USFWS_2017_
STALBiOp_NOV2017BB.pdf.
5 Draft available at: https://www.pcouncil.org/
documents/2020/05/f-1-attachment-8-pacific-coastgroundfish-fishery-2021-2022-harvestspecifications-and-management-measuresanalytical-document-organized-as-a-draftenvironmental-assessment-chapters-1-5electroni.pdf/.
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Assistant Administrator has determined
that this proposed rule is consistent
with the PCGFMP, 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 PCGFMP. 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
PCGFMP establish a procedure by
which the tribes with treaty fishing
rights in the area covered by the
PCGFMP request new allocations or
regulations specific to the tribes, in
writing, before the first of the two
meetings at which the Council considers
groundfish management measures. The
regulations at 50 CFR 660.324(d) further
direct NMFS to develop tribal
allocations and regulations in
consultation with the affected tribes.
The tribal management measures in this
proposed rule have been developed
following these procedures. The tribal
representative on the Council made a
motion to adopt the non-whiting tribal
management measures, which was
passed by the Council. Those
management measures, which were
developed and proposed by the tribes,
are included in this proposed rule.
This proposed rule has been
determined to be 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.
NMFS prepared an integrated
Analysis for this action, which
addresses the statutory requirements of
the Magnuson-Stevens Act, the National
Environmental Policy Act, Presidential
Executive Order 12866, and the
Regulatory Flexibility Act. 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
an EIS was prepared for the 2015–16
biennial harvest specifications and
management measures and is available
from NMFS (see ADDRESSES). This EIS
examined the harvest specifications and
management measures for 2015–16 and
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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 2021–22 cycle
tiers from the 2015–16 EIS and focuses
on the harvest specifications and
management measures that were not
within the scope of the 10-year
projections in the 2015–16 EIS. A copy
of the EA is available from NMFS (see
ADDRESSES). This action also announces
a public comment period on the EA.
The Chief Counsel for Regulation of
the Department of Commerce certified
to the Chief Counsel for Advocacy of the
Small Business Administration that this
proposed rule, if adopted, would not
have a significant economic impact on
a substantial number of small entities.
The purpose of this proposed rule is to
conserve Pacific Coast groundfish stocks
by preventing overfishing, while still
allowing harvest opportunity among the
various fishery sectors. This will be
accomplished by implementing the
2021–2022 annual specifications in the
U.S. exclusive economic zone off the
West Coast. The harvest specifications
affect large and small entities similarly,
and for this biennium, many of the
catch limits are proposed to increase,
providing benefit to all participants.
Additionally, this proposed rule
contains several of new management
measures that are likely to benefit
vessels, specifically openings of
previously closed fishing grounds. As a
result, an initial regulatory flexibility
analysis is not required and none has
been prepared.
List of Subjects in 50 CFR Part 660
Fisheries, Fishing, Reporting and
recordkeeping requirements.
Dated: September 28, 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.
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2. In § 660.11, amend the definition of
‘‘North-South management area’’ by
revising paragraph (2)(xviii) to read as
follows:
■
§ 660.11
General definitions.
*
*
*
*
*
North-South management area * * *
(2) * * *
(xviii) Point Arena, CA—management
line—38°57.50′ N lat.
*
*
*
*
*
■ 3. In § 660.40, revise the section
heading, removing paragraph (a),
redesignating paragraph (b) as paragraph
(a), and add a reserved paragraph (b) to
read as follows:
§ 660.40
Rebuilding plans.
*
*
*
*
*
■ 4. In § 660.50, revise paragraphs
(f)(2)(ii) and (f)(6) to read as follows:
§ 660.50 Pacific Coast treaty Indian
fisheries.
*
*
*
*
*
(f) * * *
(2) * * *
(ii) The Tribal allocation is 689.2 mt
in 2021 and 656.6 mt in 2022 per year.
This allocation is, for each year, 10
percent of the Monterey through
Vancouver area (North of 36° N lat.)
ACL. The Tribal allocation is reduced
by 1.7 percent for estimated discard
mortality.
*
*
*
*
*
(6) Petrale sole. For petrale sole, treaty
fishing vessels are restricted to a
fleetwide harvest target of 350 mt each
year.
*
*
*
*
*
■ 5. Amend § 660.71 as follows:
■ a. Redesignate paragraphs (o)(133)
through (216) as paragraphs (o)(135)
through (218); and
■ b. Add new paragraphs (o)(133) and
(134).
The additions read as follows:
§ 660.71 Latitude/longitude coordinates
defining the 10-fm (18-m) through 40-fm (73m) depth contours.
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*
*
*
*
*
(o) * * *
(133) 37°25.00′ N lat., 122°38.66′ W
long.;
(134) 37°20.68′ N lat., 122°36.79′ W
long.;
*
*
*
*
*
■ 6. Amend § 660.73 as follows:
■ a. Revise paragraphs (a)(309) through
(315);
■ b. Add paragraphs (a)(316) through
(321);
■ c. Revise paragraphs (b)(1) through
(14);
■ d. Add paragraph (b)(15);
■ e. Revise paragraphs (c)(10) through
(14);
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f. Redesignate paragraphs (d) through
(l) as paragraphs (e) through (m); and
■ g. Add new paragraph (d).
The revisions and additions read as
follows:
■
§ 660.73 Latitude/longitude coordinates
defining the 100 fm (183 m) through 150 fm
(274 m) depth contours.
*
*
*
*
*
(a) * * *
(309) 33°2.81′ N lat., 117°21.17′ W
long.;
(310) 33°1.76′ N lat., 117°20.51′ W
long.;
(311) 32°59.90′ N lat., 117°19.38′ W
long.;
(312) 32°57.29′ N lat., 117°18.94′ W
long.;
(313) 32°56.15′ N lat., 117°19.54′ W
long.;
(314) 32°55.30′ N lat., 117°19.38′ W
long.;
(315) 32°54.27′ N lat., 117°17.17′ W
long.;
(316) 32°52.94′ N lat., 117°17.11′ W
long.;
(317) 32°52.66′ N lat., 117°19.67′ W
long.;
(318) 32°50.95′ N lat., 117°21.17′ W
long.;
(319) 32°47.11′ N lat., 117°22.98′ W
long.;
(320) 32°45.60′ N lat., 117°22.64′ W
long.; and
(321) 32°42.79′ N lat., 117°21.16′ W
long.
(b) * * *
(1) 33°04.80′ N lat., 118°37.90′ W
long.;
(2) 33°02.65′ N lat., 118°34.08′ W
long.;
(3) 32°55.80′ N lat., 118°28.92′ W
long.;
(4) 32°55.04′ N lat., 118°27.68′ W
long.;
(5) 32°49.79′ N lat., 118°20.87′ W
long.;
(6) 32°48.05′ N lat., 118°19.62′ W
long.;
(7) 32°47.41′ N lat., 118°21.86′ W
long.;
(8) 32°44.03′ N lat., 118°24.70′ W
long.;
(9) 32°47.81′ N lat., 118°30.20′ W
long.;
(10) 32°49.79′ N lat., 118°32.00′ W
long.;
(11) 32°53.36′ N lat., 118°33.23′ W
long.;
(12) 32°55.13′ N lat., 118°35.31′ W
long.;
(13) 33°00.22′ N lat., 118°38.68′ W
long.;
(14) 33°03.13′ N lat., 118°39.59′ W
long.; and
(15) 33°04.80′ N lat., 118°37.90′ W
long.
(c) * * *
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(10) 33°18.14′ N lat., 118°27.94′ W
long.;
(11) 33°19.84′ N lat., 118°32.22′ W
long.;
(12) 33°20.81′ N lat., 118°32.91′ W
long.;
(13) 33°21.94′ N lat., 118°32.03′ W
long.;
(14) 33°23.14′ N lat., 118°30.12′ W
long.;
*
*
*
*
*
(d) The 100 fm (183 m) depth contour
around the northern Channel Islands off
the state of California is defined by
straight lines connecting all of the
following points in the order stated:
(1) 34°12.89′ N lat., 120°29.31′ W
long.;
(2) 34°10.96′ N lat., 120°25.19′ W
long.;
(3) 34°08.74′ N lat., 120°18.00′ W
long.;
(4) 34°07.02′ N lat., 120°10.45′ W
long.;
(5) 34°06.75′ N lat., 120°05.09′ W
long.;
(6) 34°08.15′ N lat., 119°54.96′ W
long.;
(7) 34°′07.17 N lat., 119°48.54′ W
long.;
(8) 34°05.66′ N lat., 119°37.58′ W
long.;
(9) 34°04.76′ N lat., 119°26.28′ W
long.;
(10) 34°02.93′ N lat., 119°18.06′ W
long.;
(11) 34°00.97′ N lat., 119°18.78′ W
long.;
(12) 33°59.38′ N lat., 119°21.71′ W
long.;
(13) 33°58.62′ N lat., 119°32.05′ W
long.;
(14) 33°57.69′ N lat., 119°33.38′ W
long.;
(15) 33°57.40′ N lat., 119°35.84′ W
long.;
(16) 33°56.07′ N lat., 119°41.10′ W
long.
(17) 33°55.54′ N lat., 119°47.99′ W
long.;
(18) 33°56.60′ N lat., 119°51.40′ W
long.;
(19) 33°55.56′ N lat., 119°53.87′ W
long.;
(20) 33°54.40′ N lat., 119°53.74′ W
long.;
(21) 33°52.72′ N lat., 119°54.62′ W
long.;
(22) 33°47.95′ N lat., 119°53.50′ W
long.;
(23) 33°45.75′ N lat., 119°51.04′ W
long.;
(24) 33°40.18′ N lat., 119°50.36′ W
long.;
(25) 33°38.19′ N lat., 119°57.85′ W
long.;
(26) 33°44.92′ N lat., 120°02.95′ W
long.;
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(27) 33°48.90′ N lat., 120°05.34′ W
long.;
(28) 33°51.64′ N lat., 120°08.11′ W
long.;
(29) 33°58.31′ N lat., 120°27.99′ W
long.;
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(30) 34°03.23′ N lat., 120°34.34′ W
long.;
(31) 34°09.42′ N lat., 120°37.64′ W
long.; and
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(32) 34°12.89′ N lat., 120°29.31′ W
long.
*
*
*
*
*
■ 7. Tables 1a through 1c to subpart C
are revised to read as follows:
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6. Tables 2a through 2c to subpart C
are revised to read as follows:
■
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7. In § 660.140, revise paragraphs
(d)(1)(ii)(D) to read as follows:
■
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§ 660.140
*
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Shorebased IFQ Program.
*
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(d) * * *
(1) * * *
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(ii) * * *
(D) Pacific whiting and non-whiting
QP shorebased trawl allocations. For the
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trawl fishery, NMFS will issue QP based
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on the following shorebased trawl
allocations:
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*
*
VerDate Sep<11>2014
*
*
22:18 Oct 01, 2020
8. Revise Tables 1 (North) and 1
(South) to subpart D to read as follows:
■
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*
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9. In § 660.231, revise paragraph
(b)(3)(i) to read as follows:
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■
§ 660.231 Limited entry fixed gear
sablefish primary fishery.
*
*
*
*
*
(b) * * *
(3) * * *
(i) A vessel participating in the
primary season will be constrained by
the sablefish cumulative limit
associated with each of the permits
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registered for use with that vessel.
During the primary season, each vessel
authorized to fish in that season under
paragraph (a) of this section may take,
retain, possess, and land sablefish, up to
the cumulative limits for each of the
permits registered for use with that
vessel (i.e., stacked permits). If multiple
limited entry permits with sablefish
endorsements are registered for use with
a single vessel, that vessel may land up
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62531
to the total of all cumulative limits
announced in this paragraph for the
tiers for those permits, except as limited
by paragraph (b)(3)(ii) of this section.
Up to 3 permits may be registered for
use with a single vessel during the
primary season; thus, a single vessel
may not take and retain, possess or land
more than 3 primary season sablefish
cumulative limits in any one year. A
vessel registered for use with multiple
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limited entry permits is subject to per
vessel limits for species other than
sablefish, and to per vessel limits when
participating in the daily trip limit
fishery for sablefish under § 660.232. In
2021, the following annual limits are in
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effect: Tier 1 at 58,649 lb (26,602 kg),
Tier 2 at 26,659 lb (12,092 kg), and Tier
3 at 15,234 lb (6,910 kg). In 2022 and
beyond, the following annual limits are
in effect: Tier 1 at 55,858 lb (25,337 kg),
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Tier 2 at 25,390 lb (11,517 kg), and Tier
3 at 14,509 lb (6,581 kg).
*
*
*
*
*
■ 10. Revise Tables 2 (North) and 2
(South) to subpart E to read as follows:
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11. Revise Tables 3 (North) and 3
(South) to subpart F to read as follows:
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12. Amend § 660.360 by revising
paragraphs (c)(1) introductory text,
(c)(1)(i)(B), (C), and (D), (c)(2)(i)(B) and
(D), (c)(3)(i)(A), and (c)(3)(ii)(B) to read
as follows:
■
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§ 660.360 Recreational fishery—
management measures.
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(c) * * *
(1) Washington. For each person
engaged in recreational fishing off the
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coast of Washington, the groundfish bag
limit is 9 groundfish per day, including
rockfish, cabezon and lingcod. Within
the groundfish bag limit, there are sublimits for rockfish, lingcod, and cabezon
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outlined in paragraph (c)(1)(i)(D) of this
section. In addition to the groundfish
bag limit of 9, there will be a flatfish
limit of 5 fish, not to be counted
towards the groundfish bag limit but in
addition to it. The recreational
groundfish fishery will open the second
Saturday in March through the third
Saturday in October for all species. In
the Pacific halibut fisheries, retention of
groundfish is governed in part by
annual management measures for
Pacific halibut fisheries, which are
published in the Federal Register. The
following seasons, closed areas, sublimits and size limits apply:
(i) * * *
(B) South coast recreational yelloweye
rockfish conservation area. Recreational
fishing for groundfish and halibut is
allowed within the South Coast
Recreational YRCA. The South Coast
Recreational YRCA is defined by
latitude and longitude coordinates
specified at § 660.70.
(C) Westport offshore recreational
yelloweye rockfish conservation area.
Recreational fishing for groundfish and
halibut is allowed within the Westport
Offshore Recreational YRCA. The
Westport Offshore Recreational YRCA is
defined by latitude and longitude
coordinates specified at § 660.70.
(D) Recreational rockfish conservation
area. Fishing for groundfish with
recreational gear is prohibited within
the recreational RCA unless otherwise
stated. It is unlawful to take and retain,
possess, or land groundfish taken with
recreational gear within the recreational
RCA unless otherwise stated. A vessel
fishing in the recreational RCA may not
be in possession of any groundfish
unless otherwise stated. [For example, if
a vessel participates in the recreational
salmon fishery within the RCA, the
vessel cannot be in possession of
groundfish while in the RCA. The vessel
may, however, on the same trip fish for
and retain groundfish shoreward of the
RCA on the return trip to port.]
Coordinates approximating boundary
lines at the 10- fm (18 m) through 40fm (73-m) depth contours can be found
at § 660.71. The Washington
recreational fishing season structure is
as follows:
*
vessel fishing in the recreational RCA
may not be in possession of any
groundfish. [For example, if a vessel
fishes in the recreational salmon fishery
within the RCA, the vessel cannot be in
possession of groundfish while within
the RCA. The vessel may, however, on
the same trip fish for and retain
groundfish shoreward of the RCA on the
return trip to port.] Off Oregon, from
January 1 through December 31,
recreational fishing for groundfish is
allowed in all depths. Coordinates
approximating boundary lines at the 10-
fm (18 m) through 40-fm (73-m) depth
contours can be found at § 660.71.
*
*
*
*
*
(D) In the Pacific halibut fisheries.
Retention of groundfish is governed in
part by annual management measures
for Pacific halibut fisheries, which are
published in the Federal Register.
Between the Columbia River and
Humbug Mountain, during days open to
the ‘‘all-depth’’ sport halibut fisheries,
when Pacific halibut are onboard the
vessel, no groundfish, except sablefish,
Pacific cod, and other species of flatfish
*
*
*
*
(2) * * *
(i) * * *
(B) Recreational rockfish conservation
area (RCA). Fishing for groundfish with
recreational gear is prohibited within
the recreational RCA, a type of closed
area or groundfish conservation area,
except with long-leader gear (as defined
at § 660.351). It is unlawful to take and
retain, possess, or land groundfish taken
with recreational gear within the
recreational RCA, except with longleader gear (as defined at § 660.351). A
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(sole, flounder, sanddab), may be taken
and retained, possessed or landed,
except with long-leader gear (as defined
at § 660.351). ‘‘All-depth’’ season days
are established in the annual
management measures for Pacific
halibut fisheries, which are published in
the Federal Register and are announced
on the NMFS Pacific halibut hotline, 1–
800–662–9825.
*
*
*
*
*
(3) * * *
(i) * * *
(A) Recreational rockfish conservation
areas. The recreational RCAs are areas
that are closed to recreational fishing for
groundfish. Fishing for groundfish with
recreational gear is prohibited within
the recreational RCA, except that
recreational fishing for species in the
Other Flatfish complex, petrale sole,
and starry flounder is permitted within
the recreational RCA as specified in
paragraph (c)(3)(iv) of this section. It is
unlawful to take and retain, possess, or
land groundfish taken with recreational
gear within the recreational RCA, unless
otherwise authorized in this section. A
vessel fishing in the recreational RCA
may not be in possession of any species
prohibited by the restrictions that apply
within the recreational RCA. For
example, if a vessel fishes in the
recreational salmon fishery within the
RCA, the vessel cannot be in possession
of rockfish while in the RCA. The vessel
may, however, on the same trip fish for
and retain rockfish shoreward of the
RCA on the return trip to port. If the
season is closed for a species or species
group, fishing for that species or species
group is prohibited both within the
recreational RCA and shoreward of the
recreational RCA, unless otherwise
authorized in this section. Coordinates
approximating boundary lines at the 10fm (18 m) through 40-fm (73-m) depth
contours can be found at § 660.71. The
California recreational fishing season
structure and RCA depth boundaries by
management area and month are as
follows:
*
Complex fish per day coastwide, with a
sub-bag limit of 5 fish for vermilion
rockfish. This sub-bag limit counts
towards the bag limit for the RCG
Complex and is not in addition to that
limit. Retention of yelloweye rockfish,
bronzespotted rockfish, and cowcod is
prohibited. Multi-day limits are
authorized by a valid permit issued by
California and must not exceed the daily
limit multiplied by the number of days
in the fishing trip.
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BILLING CODE 3510–22–P
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(ii) * * *
(B) Bag limits, hook limits. In times
and areas when the recreational season
for the RCG Complex is open, there is
a limit of 2 hooks and 1 line when
fishing for the RCG complex and
lingcod. The bag limit is 10 RCG
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Agencies
[Federal Register Volume 85, Number 192 (Friday, October 2, 2020)]
[Proposed Rules]
[Pages 62492-62537]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2020-21783]
[[Page 62491]]
Vol. 85
Friday,
No. 192
October 2, 2020
Part VI
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 660
Magnuson-Stevens Act Provisions; Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery; Pacific Coast Groundfish Fishery
Management Plan; Amendment 29; 2021-22 Biennial Specifications and
Management Measures; Proposed Rule
Federal Register / Vol. 85 , No. 192 / Friday, October 2, 2020 /
Proposed Rules
[[Page 62492]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 660
[Docket No. 200928-0257]
RIN 0648-BJ74
Magnuson-Stevens Act Provisions; Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery; Pacific Coast Groundfish Fishery
Management Plan; Amendment 29; 2021-22 Biennial Specifications and
Management Measures
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Proposed rule; request for comments.
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SUMMARY: This proposed rule would establish the 2021-22 harvest
specifications for groundfish 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 and the
Pacific Coast Groundfish Fishery Management Plan (PCGFMP). This
proposed rule would also revise the management measures that are
intended to keep the total annual catch of each groundfish stock or
stock complex within the annual catch limits. These proposed measures
are intended to help prevent overfishing, rebuild overfished stocks,
achieve optimum yield, and ensure that management measures are based on
the best scientific information available. Additionally, this proposed
rule announces the receipt of exempted fishing permit applications.
NMFS has made a preliminary determination that these applications
warrant further consideration. NMFS requests public comment on these
applications. This action also would implement Amendment 29 to the
PCGFMP, which would designate shortbelly rockfish as an ecosystem
component species, and would make changes to the trawl/non-trawl
allocations for blackgill rockfish within the southern slope complex
south of 40[deg]10' North latitude (N lat.), petrale sole, lingcod
south of 40[deg]10' N lat., and widow rockfish.
DATES: Comments must be received no later than November 2, 2020.
ADDRESSES: Submit your comments, identified by NOAA-NMFS-2020-0098, by
either of the following methods:
Federal e-Rulemaking Portal: Go to www.regulations.gov/#!docketDetail;D=NOAA-NMFS-2020-0098, click the ``Comment Now!'' icon,
complete the required fields, and enter or attach your comments. The
exempted fishing permit (EFP) applications will be available under
Supporting Documents through the same link.
Mail: Submit written comments to Barry Thom, Regional
Administrator, West Coast Region, NMFS, 7600 Sand Point Way NE,
Seattle, WA 98115-0070.
Instructions: NMFS may not consider comments if they are sent by
any other method, to any other address or individual, or received after
the comment period ends. All comments received are a part of the public
record and NMFS will post 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 is publicly
accessible. NMFS will accept anonymous comments (enter ``N/A'' in the
required fields if you wish to remain anonymous).
Electronic Access
This 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 West Coast Region website at https://www.westcoast.fisheries.noaa.gov/fisheries/groundfish/ and at
the Pacific Fishery Management Council's website at https://www.pcouncil.org. The final 2020 Stock Assessment and Fishery
Evaluation (SAFE) report for Pacific Coast groundfish, as well as the
SAFE reports for previous years, are available from the Pacific Fishery
Management Council's website at https://www.pcouncil.org.
FOR FURTHER INFORMATION CONTACT: Karen Palmigiano, phone: 206-526-4491
or email: [email protected].
SUPPLEMENTARY INFORMATION:
I. Background
Chapter 5 of the Pacific Coast Groundfish Fishery Management Plan
(PCGFMP) requires the Pacific Fishery Management Council (Council) to
assess the biological, social, and economic conditions of the Pacific
coast groundfish fishery and use this information to develop harvest
specifications and management measures at least biennially. This
proposed rule is based on the Council's final recommendations for
harvest specifications and management measures for the 2021-22 biennium
made at its April and June 2020 meetings.
The Council deemed the proposed regulations necessary and
appropriate to implement these actions in an August, 26, 2020, letter
from Council Executive Director, Chuck Tracy, to Regional Administrator
Barry Thom. Under the Magnuson-Stevens Fishery Conservation and
Management Act (Magnuson-Stevens Act), NMFS is required to publish
proposed rules for comment after preliminarily determining whether they
are consistent with applicable law. We are seeking comment on the
proposed regulations in this action and whether they are consistent
with the PCGFMP, the Magnuson-Stevens Act and its National Standards,
and other applicable law.
Concurrent with this proposed rule, NMFS also published a Notice of
Availability (NOA) to announce the proposed Amendment 29 to the PCGFMP.
The NOA requests public review and comment on proposed changes to the
Council fishery management plan document (85 FR 54529; September 2,
2020).
A. Specification and Management Measure Development Process
The Northwest Fisheries Science Center (NWFSC) conducted full stock
assessments in 2019 for 7 of the 128 stocks \1\ currently included
under the PCGFMP as stocks that require conservation and management
(cabezon, big skate, longnose skate, sablefish, cowcod, gopher
rockfish, and black-and-yellow rockfish). Additionally, the NWFSC
reviewed assessment updates for Petrale sole and widow rockfish, as
well as catch-only assessment updates for a number of previously
assessed stocks (black rockfish, blackgill rockfish, California blue/
deacon rockfish north of Point Conception, canary rockfish, China
rockfish, darkblotched rockfish, Dover sole, lingcod, longspine
thornyheads, rougheye and blackspotted rockfishes, and shortspine
thornyhead). The NWFSC did not update assessments for the remaining
stocks, so harvest
[[Page 62493]]
specifications for these stocks are based on assessments from previous
years. The full stock assessments used to set catch limits for this
biennium are available on the Council website (https://www.pcouncil.org/).
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\1\ Stocks for which annual catch limits (ACLs) or ACL
contributions to stock complex ACLs are calculated. Assessments do
not include stocks designated as ecosystem component species.
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The Council's stock assessment review panel (STAR panel) reviewed
the stock assessments, including assessments on stocks for which some
biological indicators are available, as described below, for technical
merit, and to determine that each stock assessment document was
sufficiently complete. Finally, the Council's Scientific and
Statistical Committee (SSC) reviewed the stock assessments and STAR
panel reports and made its recommendations to the Council (Agenda Item
H.5, September 2019 Council Meeting).
The Council considered the new stock assessments, stock assessment
updates, catch-only updates, public comment, recommendations from the
SSC, and advice from its advisory bodies over the course of six Council
meetings during development of its recommendations for the 2021-22
harvest specifications and management measures. At each Council meeting
between June 2019 and June 2020, the Council made a series of decisions
and recommendations that were, in some cases, refined after further
analysis and discussion. Table 2 in the Analysis describes the
Council's meeting schedule for developing the 2021-22 biennial harvest
specifications. Additionally, detailed information, including the
supporting documentation the Council considered at each meeting, is
available at the Council's website, www.pcouncil.org.
The 2021-22 biennial management cycle was the third cycle following
PCGFMP Amendment 24 (80 FR 12567, March 10, 2015), which established
default harvest control rules and was analyzed through an Environmental
Impact Statement (EIS) (Final Environmental Impact Statement for
Pacific Coast Groundfish Harvest Specifications and Management Measures
for 2015-2016 and Biennial Periods Thereafter, and Amendment 24 to the
PCGFMP, published January 2015). The EIS described the ongoing
implementation of the PCGFMP and default harvest control rules, along
with 10-year projections for harvest specifications and a range of
management measures. Under Amendment 24, the default harvest control
rules used to determine the previous biennium's harvest specifications
(i.e., overfishing limits [OFLs], acceptable biological catches (ABCs),
and annual catch limits [ACLs]) are applied automatically to the best
scientific information available to determine the future biennium's
harvest specifications. NMFS implements harvest specifications based on
the default harvest control rules used in the previous biennium unless
the Council makes a recommendation to deviate from the default.
Therefore, this rule implements the default harvest control rules,
consistent with the last biennium (2019-20), for most stocks, and
discusses Council-recommended departures from the defaults. The
Analysis supporting this action identifies the preferred harvest
control rules, management measures, and other management changes that
were not described in the 2015 EIS, and will be posted on the NMFS West
Coast Region web page (see Electronic Access).
Information regarding the OFLs, ABCs, and ACLs proposed for
groundfish stocks and stock complexes in 2021-22 is presented below,
followed by a discussion of the proposed management measures for
commercial and recreational groundfish fisheries.
II. Proposed Harvest Specifications
This proposed rule would set 2021-22 harvest specifications and
management measures for 127 of the 128 groundfish stocks which
currently have ACLs or ACL contributions to stock complexes managed
under the PCGFMP, except for Pacific whiting. Pacific whiting harvest
specifications are established annually through a separate bilateral
process with Canada. Shortbelly rockfish, which is currently managed
with harvest specifications, would no longer be managed with harvest
specifications beginning in the 2021-22 biennium and would instead be
classified as an ecosystem component species. The change to shortbelly
management is made through Amendment 29 to the PCGFMP and is discussed
in detail in the NOA for that amendment. Public comment is open on the
NOA (see ADDRESSES).
The proposed OFLs, ABCs, and ACLs are based on the best available
biological and socioeconomic data, including projected biomass trends,
information on assumed distribution of stock biomass, and revised
technical methods used to calculate stock biomass. The PCGFMP specifies
a series of three stock categories for the purpose of setting maximum
sustainable yield (MSY) \2\, OFLs, ABCs, ACLs, and rebuilding
standards. Category one represents the highest level of information
quality available, while category three represents the lowest. Category
one stocks are the relatively few stocks for which the NWFSC can
conduct a ``data rich'' quantitative stock assessment that incorporates
catch-at-age, catch-at-length, or other data. The SSC can generally
calculate OFLs and overfished/rebuilding thresholds for these stocks,
as well as ABCs, based on the uncertainty of the biomass estimated
within an assessment or the variance in biomass estimates between
assessments for all stocks in this category. The set of category two
stocks includes a large number of stocks for which some biological
indicators are available, yet status is based on a ``data-moderate''
quantitative stock assessment. The category three stocks include minor
stocks which are caught, but for which there is, at best, only
information on landed biomass. For stocks in this category, there is
limited data available for the SSC to quantitatively determine MSY,
OFL, or an overfished threshold. Typically, catch-based methods (e.g.,
depletion-based stock reduction analysis, depletion corrected average
catch, and average catches) are used to determine the OFL for category
three stocks. A detailed description of each of these categories can be
found in Section 4.2 of the PCGFMP.
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\2\ MSY is the largest long-term average catch that can be taken
from a fish stock under prevailing environmental and fishery
conditions.
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A. Proposed OFLs for 2021 and 2022
The OFL serves as the maximum amount of fish that can be caught in
a year without resulting in overfishing. Overfishing occurs when a
stock has a harvest rate, denoted as Fx, is set
higher than the rate that produces the stock's MSY. The SSC derives
OFLs for groundfish stocks with stock assessments by applying the
harvest rate to the current estimated biomass (B). Harvest rates
represent the rates of fishing mortality (F) that will reduce the
female spawning potential ratio (SPR) to X percent of its unfished
level. As an example, a harvest rate of F40 is more
aggressive than F45 or F50
harvest rates because F40 allows more fishing
mortality on a stock (as it allows a harvest rate that would reduce the
stock to 40 percent of its unfished level). The OFL does not account
for scientific or management uncertainty, so the SSC typically
recommends an ABC that is lower than the OFL in order to account for
this uncertainty. Usually, the greater the amount of scientific
uncertainty, the lower the ABC is set compared to the OFL.
For 2021-22, the Council maintained its policy of using a default
harvest rate as a proxy for the fishing mortality rate that is expected
to achieve FMSY. The Council also maintained the same
default harvest rate proxies as used in
[[Page 62494]]
the 2019-20 biennium, based on the SSC's recommendations:
F30 for flatfish (meaning an SRP harvest rate that
would reduce the stock to 30 percent of its unfished level),
F50 for rockfish (including longspine and shortspine
thornyheads), F50 for elasmobranchs, and
F45for other groundfish such as sablefish and
lingcod. For unassessed stocks, the Council recommended using a
historical catch-based approach (e.g., average catch, depletion-
corrected average catch, or depletion-based stock reduction analysis)
to set the OFL. See Tables 1a and 2a to Part 660, Subpart C in the
proposed regulatory text supporting this rule for the proposed 2021-22
OFLs.
A detailed description of the scientific basis for all of the SSC-
recommended OFLs proposed in this rule is included in the SAFE document
for 2020, available at the Council's website, www.pcouncil.org.
B. Proposed ABCs for 2021 and 2022
The ABC is the stock or stock complex's OFL reduced by an amount
associated with scientific uncertainty. The SSC-recommended P star-
sigma approach determines the amount by which the OFL is reduced to
account for this uncertainty. Under this approach, the SSC recommends a
sigma ([sigma]) value. The [sigma] value is generally based on the
scientific uncertainty in the biomass estimates generated from stock
assessments and is usually related to the stock category. After the SSC
determines the appropriate [sigma] value, the Council chooses a P star
(P*) based on its chosen level of risk aversion considering the
scientific uncertainties. A P* of 0.5 equates to no additional
reduction for scientific uncertainty beyond the [sigma] value
reduction. The PCGFMP specifies that the upper limit of P* will be
0.45. The P*-sigma approach is discussed in detail in the proposed and
final rules for the 2011-12 (75 FR 67810, November 3, 2010; 76 FR
27508, May 11, 2011) and 2013-14 (77 FR 67974, November 12, 2012; 78 FR
580, January 3, 2013) biennial harvest specifications and management
measures.
The SSC recently endorsed new [sigma] values that increase the
scientific uncertainty estimate and reduce the proposed ABCs and ACLs
relative to what they could have been under the [sigma] and P* values
used in the previous biennium. The new [sigma] values, endorsed by the
Council at its March 2019 meeting, include a new base reduction for
Category 1 stocks of 0.5 and an increase in the buffer between the OFL
and ABC as the age of the assessment increases. Currently, [sigma] is
the same for each year regardless of the age of the assessment. Table 1
provides the [sigma] values used in previous biennium and the new
[sigma] values with a higher base year deduction and progressively
increasing [sigma] values with the age of the assessment.
[GRAPHIC] [TIFF OMITTED] TP02OC20.000
Based on the new methodology, the SSC quantified major sources of
scientific uncertainty in the estimates of OFLs and generally
recommended a [sigma] value of 0.5 for category one stocks (previously
0.36), a [sigma] value of 1.0 for category two stocks (previously
0.72), and a [sigma] value of 2.0 for category three stocks (previously
1.44). For category two and three stocks, there is greater scientific
uncertainty in the OFL estimate because the assessments for these
stocks are informed by less data than the assessments for category one
stocks. Therefore, the scientific uncertainty buffer is generally
greater than that recommended for stocks with data-rich stock
assessments. Assuming the same P* is applied, a larger [sigma] value
results in a larger reduction from the OFL. For 2021-22, the Council
continued the general policy of using the SSC-recommended [sigma]
values for each stock category.
For 2021-22, the Council maintained the P* policies it established
for the previous biennium for most stocks, except Oregon black
rockfish, cowcod south of 40[deg]10' N lat., sablefish, and shortbelly
rockfish. The Council considered alternative P* values for Petrale sole
but ultimately decided to stay with the default P* value used in the
previous biennium. As was done in 2015-16, 2017-18, and 2019-20, the
Council recommended using P* values of 0.45 for all individually
managed category one stocks, except sablefish and yelloweye rockfish.
Combining the category one [sigma] value of 0.5 with the P* value of
0.45 results in a reduction of 6.1 percent from the OFL when deriving
the ABC. For category two stocks, the Council's general policy was to
apply a P* of 0.4, with a few exceptions. The Council recommended
applying a P* of 0.45 for big skate, cowcod south of 34[deg]27' N lat.,
English sole, longnose skate, Pacific ocean perch, and all of the
stocks managed in the Oregon blue/deacon/black rockfish complex,
[[Page 62495]]
Nearshore Rockfish complexes, and the Other Fish complex. When combined
with the [sigma] values of 1.00 for category two, a P* value of 0.45
corresponds to an 11.8 percent reduction and a P* value of 0.40
corresponds to a 22.4 percent reduction. For category three stocks, the
Council's general policy was to apply a P* value of 0.45 for these
stocks, except the Council recommended a P* value of 0.40 for cowcod
between 40[deg]10' N lat. and 34[deg]27' N lat., Pacific cod, starry
flounder, and all stocks in the Other Flatfish complex. When combined
with the [sigma] values of 2.00 for category three, a P* value of 0.45
corresponds to 22.2 percent reduction and a P* value of 0.40
corresponds to a 39.8 percent reduction. See Tables 1-3 in Agenda Item
H.8, Supplemental Attachment 2, September 2019 Council meeting for the
full description of [sigma] and P* values by stock. See Tables 1a and
2a to Part 660, Subpart C in the in the proposed regulatory text of
this proposed rule for the proposed 2021-22 ABCs.
C. Proposed ACLs for 2019 and 2020
The Council recommends ACLs for each stock and stock complex that
is in need of conservation and management or ``in the fishery,'' as
defined in the PCGFMP. To determine the ACL for each stock, the Council
will determine the best estimate of current stock abundance and its
relation to the precautionary and overfished/rebuilding thresholds.
Under the PCGFMP, the biomass level that produces MSY, or
BMSY, is defined as the precautionary threshold. When the
biomass for an assessed category one or two stock falls below
BMSY, the ACL is set below the ABC using a harvest rate
reduction to help the stock return to the BMSY level, which
is the management target for groundfish stocks. If a stock biomass is
larger than BMSY, the ACL may be set equal to the ABC, or
the ACL may be set below the ABC to address conservation objectives,
socioeconomic concerns, management uncertainty, or other factors
necessary to meet management objectives. The overfished/rebuilding
threshold is 25 percent of the estimated unfished biomass level for
non-flatfish stocks or 50 percent of BMSY, if known. The
overfishing/rebuilding threshold for flatfish stocks is 12.5 percent of
the estimated unfished biomass level. When a stock is below
BMSY (the precautionary threshold) but above the
overfishing/rebuilding threshold, it is considered to be in the
precautionary zone.
Under PCGFMP Amendment 24, the Council set up default harvest
control rules, which established default policies that would be applied
to the best available scientific information to set ACLs each biennial
cycle, unless the Council has reasons to diverge from that harvest
control rule. A complete description of the default harvest control
rules for setting ACLs is described in the proposed and final rule for
the 2015-16 harvest specifications and management measures and PCGFMP
Amendment 24 (80 FR 687, January 6, 2015; 80 FR 12567, March 10, 2015).
The PCGFMP defines the 40-10 harvest control rule for stocks with a
BMSY proxy of B40 that are in the
precautionary zone as the standard reduction. The analogous harvest
control rule with the standard reduction for assessed flatfish stocks
is the 25-5 harvest control rule for flatfish stocks with a
BMSY proxy of B25. The further the stock
biomass is below the precautionary threshold, the greater the reduction
in ACL relative to the ABC, until at B10 for a stock
with a BMSY proxy of B40, or
B5 for a stock with a BMSY proxy of
B25, the ACL would be set at zero.
Under the PCGFMP, the Council may recommend setting the ACL at a
different level than what the default harvest control rules specify as
long as the ACL does not exceed the ABC and complies with the
requirements of the Magnuson-Stevens Act (see Chapter 8 of the analysis
for information on the Magnuson-Stevens Act and other applicable laws).
For most of the stocks and all the stock complexes managed with harvest
specifications for 2021-22, the Council chose to maintain the default
harvest control rules from the previous biennial cycle. For four
stocks, Oregon Black rockfish, cowcod south of 40[deg]10' N lat.,
sablefish, and shortbelly rockfish, the Council recommended deviating
from the default harvest control rule. Table 2 presents a summary table
of the proposed changes to default harvest control rules for certain
stocks for 2021-22. Each of these changes is discussed further below.
[[Page 62496]]
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Cowcod South of 40[deg]10' N Lat.
A new cowcod assessment conducted by the NWFSC in 2019 indicated
the stock south of 40[deg]10' N lat. had transitioned from a rebuilding
stock to a stock with current depletion estimate at the start of 2019
of 57 percent of unfished spawning output (Agenda Item H.5. Attachment
9, September 2019), which is far above the precautionary threshold of
50 percent. When a stock is determined to be rebuilt, its harvest
control rule automatically reverts back to the default harvest control
rule for the next biennium. For the 2021-22 biennium, cowcod south of
40[deg]10' N lat. was the only stock declared rebuilt.
Consistent with the Council's preferred alternative, this action
proposes that the cowcod south of 40[deg]10' N lat. ACL would be set
equal to the ABC with a P* of 0.4, resulting in ACLs of 84 mt in 2021
and 82 mt in 2022. The Council recommended a lower P* value for cowcod
south of 40[deg]10' N lat. than what would have been applied under the
default P* value (P* = 0.45) to address the relatively high uncertainty
in the estimated biomass and productivity in the cowcod assessment due
to a lack of adequate data (particularly age data) for estimating
growth, natural mortality, and recruitment. The revised P* value of
0.40 is consistent with other category two stocks. See Section 2.2.2.2
of the Analysis for more information on the Council's consideration of
alternative harvest specifications for cowcod south of 40[deg]10' N
lat.
The resulting ACLs would increase by more than eight times the
amount in place in 2019 (10 mt). As an additional precaution due to the
uncertainty in the assessment, the Council also recommended, and NMFS
is proposing, an ACT of 50 mt for cowcod south of 40[deg]10' N lat. The
ACT is a management measure and is discussed further in Section III of
this preamble.
Oregon Black Rockfish
Oregon black rockfish is a category two stock, managed as part of
the Oregon blue/deacon/black rockfish complex. Oregon black rockfish
was first assessed as a single stock in 2015. In 2019, the Oregon black
rockfish stock was estimated to be at 56 percent of its unfished
spawning output. For 2021-22, the NWFSC conducted a catch-only update
to the 2015 assessment by adding realized catch data from 2015-2018 and
estimates of catch for 2019 and 2020. In Oregon, realized catches were
closer to projected catches in 2015-2017, but lower in 2018 resulting
in OFL projections for 2021 and 2022 that are slightly higher than the
projections in the previous assessment. In addition to the catch data
update, the SSC applied the newly endorsed [sigma] values to each year
in the forecast (as discussed above in B. Proposed ABCs for 2021 and
2022). Because Oregon black rockfish is a category two stock, a base
[sigma] value of 1.0 was applied to years 2021-2030 (Table 1-2 in
Agenda Item H.5, Attachment 15, September 2019). Black rockfish was
last assessed in 2015, so the stock is also subject to further [sigma]
value reductions. However, the Council recommended and NMFS is
proposing a
[[Page 62497]]
phased-in approach to incorporating this additional ABC reduction.
Black rockfish is the primary target for the Oregon recreational
and commercial nearshore fisheries. In 2017, Oregon recreational
fisheries were shut down early because of black rockfish concerns, and
the Council received public testimony as to the severe negative
consequences for charter business operators and tourist-revenue
dependent coastal communities resulting from this closure. Due to the
constraining nature of black rockfish in Oregon and the biomass level
being above the precautionary threshold, the Oregon Department of Fish
and Wildlife (ODFW) requested the Council consider an alternative for
the 2021-22 biennium where the 2020 ABC (512 mt) is specified for 2021
and 2022, and the ACLs are set equal to ABCs. The Magnuson-Stevens Act
and the PCGFMP allow the SSC to recommend an ABC that differs from the
ABC control rule on a case by case basis, provided the SSC offers
justification for its recommended deviation. In 2023, the current
default harvest control rule (ABC = ACL, P* of 0.45) would once again
apply to Oregon black rockfish. In this case, long-term projections
under the Council's default harvest control rule and the alternative
2021 and 2022 ABC both result in a projected stock biomass at 54
percent of its unfished spawning output in 2030. Stocks with biomass
estimates greater than 40 percent depletion are above the precautionary
thresholds in the PCGFMP. Because the biomass is the same under either
option, the SSC recommended the alternative 2021 and 2022 ABC.
Therefore based on the Analysis, the Council has recommended and
NMFS is proposing alternative harvest specifications for Oregon black
rockfish as part of the Oregon blue/deacon/black rockfish complex. The
alternative harvest control rule would implement an ACL for the 2021
and 2022 biennium of 512 mt in each year. This ACL contributes to the
overall stock complex ACL.
Sablefish
The NWFSC completed a full stock assessment for sablefish in 2019
(Agenda Item H.5. Attachment 7, September 2019). In 2019, the sablefish
stock is estimated to be at 39 percent of unfished spawning output.
However, biomass is projected to increase, and the spawning output is
projected to be above the precautionary threshold (B40) in
2021. The expected increase in biomass is driven in part by the
estimated, but highly uncertain, size of the 2016 year class. Now that
sablefish biomass is projected to be above BMSY, the Council
considered alternative harvest specifications for the 2021-22 biennium.
Additionally, the Council recommended revising the apportionment of
the ACL north and south 36[deg] N Lat. Each biennium, the coastwide
sablefish ABC is apportioned to ACLs for the areas north and south of
36[deg] N Lat. based on a percentage. In 2019-20, the Council used the
average swept area biomass from the trawl survey to determine this
percentage. However, for the 2021-22 biennium, the Council recommended
updating its methods for determining this percentage and will now be
using a rolling 5-year average of the swept area biomass instead of the
long-term average. This results in an increase in the percentage of the
sablefish apportioned north of 36[deg] N Lat. ACL from 73.7 percent to
78.4 percent and a decrease in the percentage of the sablefish
apportioned south of 36[deg] N Lat. ACL from 26.3 percent to 21.5
percent. The change in apportionment of the north and south sablefish
ACLs is expected to result in higher attainment of both of the ACLs and
should better align with recent catches by area.
Under the default harvest control rule, the ABC would be set equal
to the ACL with a P* value of 0.4. The P* value of 0.4 was set when the
unfished spawning output was below 40 percent. Under a P* value of 0.4,
the unfished spawning output is estimated to be at 46 percent in 2021
and 47 percent by 2030 assuming full ACL removals each year. The ACLs
would no longer be subject to the 40-10 rule reduction because the
stock would be above the BMSY proxy in 2021 and would
therefore be set equal to the ABC. The ACLs under the default harvest
control rule and the revised apportionment percentages would be 6,435
mt for north of 36[deg] N Lat. and 1,773 mt for south of 36[deg] N Lat.
in 2021. In 2022, the ACL would be 6,124 mt for north of 36[deg] N Lat.
and 1,687 mt for south of 36[deg] N Lat.
Based on the 2019 sablefish stock assessment, the Council
recommended an alternative harvest specifications for sablefish using a
P* value of 0.45 for the 2021-22 biennium. Under the increased P*
value, the unfished spawning output is estimated to be at 46 percent in
2021 and 44 percent by 2030, assuming full ACL removals each year. No
reduction to the ACL would be necessary, similar to the default,
because the stock's unfished spawning output is above 40 percent.
Therefore, under the P* value of 0.45, the 2021 ACLs for the north and
south would be 6,479 mt and 2,312, mt, respectively. The 2022 ACLs for
the north and south would be 6,172 mt and 2,203 mt, respectively.
Therefore, the Council recommended, and NMFS is proposing, to
implement an alternative harvest control rule for sablefish for the
2021-22 biennium. The alternative harvest control rule would set the
ABC equal to the ACL with a P* value of 0.45 resulting in ACLs that are
higher than under the Council's No Action default harvest control rule
for sablefish.
Shortbelly Rockfish
Shortbelly rockfish has been a topic of discussion on every Council
agenda beginning in November 2018 due to higher than anticipated
bycatch in recent years. Shortbelly rockfish is currently a species
managed within the PCGFMP in section 3.1 of the PCGFMP and directed
fishing is allowed even though it is not the target of a directed
fishery.
As part of the 2021-22 biennium, the Council recommended and NMFS
is proposing to reclassify shortbelly rockfish as an ecosystem
component species through Amendment 29 to the PCGFMP. For more
information on this reclassification, see the NOA for Amendment 29 (see
ADDRESSES).
Stocks in Rebuilding Plans
When a stock has been declared overfished, the Council must develop
and manage the stock in accordance with a rebuilding plan. For
overfished stocks in the PCGFMP, this means that the harvest control
rule for overfished stocks sets the ACL based on the rebuilding plan.
The proposed rules for the 2011-12 (75 FR 67810, November 3, 2010) and
2013-14 (77 FR 67974, November 14, 2012) harvest specifications and
management measures contain extensive discussions on the management
approach used for overfished stocks, which are not repeated here. In
addition, the SAFE document posted on the Council's website at https://www.pcouncil.org/groundfish/safe-documents/ contains a detailed
description of each overfished stock, its status and management, as
well as the SSC's approach for rebuilding analyses. This document
provides information on cowcod south of 40[deg]10' N lat., which has
rebuilt since the last biennium, and yelloweye rockfish which is the
only remaining rebuilding stock in the PCGFMP. The Council proposed
yelloweye rockfish ACLs for 2021 and 2022 based on the current
yelloweye rockfish rebuilding plan, so additional details are not
repeated here. Appendix F to the PCGFMP contains the most recent
rebuilding plan parameters, as well as a
[[Page 62498]]
history of each overfished stock, and can be found at https://www.pcouncil.org/groundfish/fisherymanagement-plan/.
Yelloweye rockfish was declared overfished in 2002. The Council
adopted a rebuilding plan for the stock in 2004, and revised the
rebuilding plan in 2011 under Amendment 16-4 to the PCGFMP, and again
during the 2019-20 biennium.
Additionally, the Council recommended, and NMFS is proposing, to
establish annual catch targets (ACTs) within the nontrawl allocation
harvest guideline (HG). The nontrawl sector includes the limited entry
fixed gear (LEFG) and open access (OA) fisheries as well as the
recreational fisheries for Washington, Oregon, and California. The
nearshore fisheries occur off of Oregon and California and are subject
to both Federal and state HGs as well as other state-specific
management measures. The non-nearshore fisheries include the limited
entry and Federal open access fixed gear fleets. Tables 3 and 4 outline
the proposed harvest specifications for 2021 and 2022 for yelloweye
rockfish.
[GRAPHIC] [TIFF OMITTED] TP02OC20.002
The Council recommended using ACTs for the nontrawl sector as a
precaution. As discussed in the Analysis, because yelloweye rockfish
catch has been restricted for many years, it is difficult to project
encounter rates. This precautionary approach to higher catch limits
would allow more access to target fisheries for the nontrawl sector,
while also managing for the uncertainty and volatility in catch of this
rebuilding stock by this sector.
D. Summary of ACL Changes From 2019 to 2021-22
Table 5 compares the ACLs for major stocks for 2019, 2020, and
2021-22. Under this proposed rule, nine stocks would have higher ACLs
in 2021 and 2022 than in 2019. Of the 43 stocks and stock complexes
managed with ACLs in 2020, 21 stocks have ACLs that would decrease in
2021 from 2020 and 12 stocks have ACLs that would be close to the
amount in place in 2020 (Table 4.6 of the Analysis). Shortbelly
rockfish are proposed to be no longer be managed with an ACL and one
stock, Pacific cod, would have the same ACLs in 2020, 2021, and 2022.
Two stocks (big skate and cowcod south of 40[deg]10' N lat.) have ACLs
that would increase more than 100 percent, and one stock complex,
Washington's cabezon/kelp greenling, has an ACL that would increase by
92.3 percent. These increases are due to new information provided in
the 2019 stock assessments for these stocks. The ACL for the shelf
rockfish north complex would decrease by 26.5 percent, which is the
largest ACL decrease between 2020 and 2021, followed by the ACL for
arrowtooth flounder, which would decrease by 22.1 percent. These
decreases are due to updated projections based on the new sigma values.
[[Page 62499]]
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[[Page 62500]]
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III. Proposed Management Measures
This section describes proposed management measures (i.e., biennial
fishery harvest guidelines and set-asides) used to further allocate the
ACLs to the various components of the fishery and control fishing.
Management measures for the commercial fishery modify fishing behavior
during the fishing year to ensure that catch does not exceed the ACL,
and include trip and cumulative landing limits, time/area closures,
size limits, and gear restrictions. Management measures for the
recreational fisheries include bag limits, size limits, gear
restrictions, fish dressing requirements, and time/area closures.
A. Deductions From the ACLs
Before making allocations to the primary commercial and
recreational components of groundfish fisheries, the Council recommends
``off-the-top deductions,'' or deductions from the ACLs to account for
anticipated mortality for certain types of activities: Harvest in
Pacific Coast treaty Indian tribal fisheries; harvest in scientific
research activities; harvest in non-groundfish fisheries (incidental
catch); and harvest that occurs under EFPs. These off-the-top
deductions are proposed for individual stocks or stock complexes and
can be found in the footnotes to Tables 1a and 2a to part 660, subpart
C. The details of the EFPs are discuss below in Section III., J.
B. Tribal Fisheries
The Quileute Tribe, Quinault Indian Nation, Makah Indian Tribe, and
Hoh Indian Tribe (collectively, ``the Pacific Coast Tribes'') implement
management measures for Tribal fisheries both independently as
sovereign governments and cooperatively with the management measures in
the Federal regulations. The Pacific Coast Tribes may adjust their
Tribal fishery management measures inseason to stay within the Tribal
harvest targets and estimated impacts to overfished stocks. Table 6
provides the proposed Tribal harvest targets proposed for the 2021-22
biennium.
[[Page 62501]]
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The Pacific Coast Tribes proposed trip limit management in Tribal
fisheries for 2021-22 for several stocks, including several rockfish
stocks and stock complexes. This rule proposes the trip limits for
Tribal fisheries as provided to the Council at its April 2020 meeting
in Supplemental Tribal Report 1, Agenda Item G.6.a. For rockfish
stocks, Tribal regulations will continue to require full retention of
all overfished rockfish stocks and marketable non-overfished rockfish
stocks. The Pacific Coast Tribes will continue to develop management
measures, including depth, area, and time restrictions, in the directed
Tribal Pacific halibut fishery in order to minimize incidental catch of
yelloweye rockfish.
C. Biennial Fishery Allocations
The Council routinely recommends 2-year trawl and nontrawl
allocations during the biennial specifications process for stocks
without formal allocations (as defined in Section 6.3.2 of the PCGFMP)
or stocks where the long-term allocation is suspended because the stock
is declared overfished. As part of the 2021-22 biennium, the Council
also decided to revise the 2-year allocations for canary rockfish, as
well as Petrale sole, widow rockfish, lingcod south of 40[deg]10' N
lat., and the slope rockfish complex south of 40[deg]10' N lat., which
were established through Amendment 21 to the PCGFMP (75 FR 32993, June
10, 2010), to better align these allocations with current harvest
trends. The changes to these allocations are proposed as part of
Amendment 29 to the PCGFMP (see I. Background).
The trawl and nontrawl allocations, with the exception of sablefish
north of 36[deg] N lat., are based on the fishery harvest guideline.
The fishery harvest guideline is the tonnage that remains after
subtracting the off-the-top deductions described in Section III., A,
entitled ``Deductions from the ACLs,'' in this preamble. The trawl and
nontrawl allocations and recreational harvest guidelines are designed
to accommodate anticipated mortality in each sector as well as
variability and uncertainty in those mortality estimates. Additional
information on the Council's allocation framework and formal
allocations can be found in Section 6.3 of the PCGFMP and Sec. 660.55
of the Federal regulations. Allocations described below are detailed in
the harvest specification tables appended to 50 CFR part 660, subpart
C, in the regulatory text of this proposed rule.
The Council's recommended and NMFS' proposed allocations are shown
Tables 1b and 2b in the proposed regulatory text for this proposed rule
and summarized below.
Big Skate
The Council recommended and NMFS is proposing the allocations shown
in Table 7 for big skate in 2021 and 2022. These allocations are
anticipated to accommodate estimates of mortality of big skate, by
sector, in 2021-22. Allocations of big skate are determined on a
biennial basis. For 2021-22, the Council elected to maintain the
current big skate split of 95 percent to the trawl fishery and 5
percent to the non-trawl fishery
[[Page 62502]]
resulting in a trawl allocation of 1,348.7 mt and a non-trawl
allocation of 71 mt in 2021 and 2022. No further allocations or
deductions are made.
[GRAPHIC] [TIFF OMITTED] TP02OC20.006
Bocaccio South of 40[deg]10' N Lat.
Specifications for bocaccio are determined through the biennial
specifications process. For 2021-22, the Council recommended and NMFS
is proposing the allocations shown in Table 8 for bocaccio in 2021 and
2022, which maintain the allocation structure from the previous
biennium. These allocations are anticipated to accommodate estimates of
mortality of bocaccio, by sector, in 2021-22. In each year, the fishery
harvest guideline is split with 39 percent going to the trawl sectors
and 61 percent to the non-trawl sectors. For the trawl sector this
results in an allocation of 663.8 mt in 2021 and 654.4 mt in 2022. The
non-trawl sectors would receive 1,036.4 mt in 2021 and 1,021.8 mt in
2022. The non-trawl allocation is then distributed between the
commercial (nearshore and non-nearshore fisheries) and California
recreational fisheries. In 2021, the commercial sector would receive
30.9 percent of the non-trawl allocation or 320.2 mt, and the
California recreational sector would receive 716.2 mt. In 2022, the
same percentage would remain in place with the commercial sector
receiving 315.7 mt and the California recreational sector receiving
706.1 mt.
[GRAPHIC] [TIFF OMITTED] TP02OC20.007
Canary Rockfish
The Council recommended and NMFS is proposing the allocations in
Table 9 for canary rockfish in 2021 and 2022, which maintain the status
quo proportions from the 2017-18 biennium, but also combine the
commercial fixed gear harvest guideline for the nearshore and non-
nearshore fisheries. These allocations are anticipated to accommodate
estimates of mortality of canary rockfish, by sector, in 2021-22. For
canary rockfish, the fishery harvest guideline is distributed to the
trawl and non-trawl sectors with trawl receiving 72.3 percent and non-
trawl sectors receiving 27.7 percent each year. In 2021, the trawl
sector would receive 917 mt of canary rockfish, of which 36 mt would be
deducted to account for bycatch in the at-sea sectors, and the
remaining 881.2 mt would be distributed to the shorebased individual
fishing quota (IFQ) sector. The non-trawl sector would receive 351.4 mt
which is distributed to the commercial nontrawl (126.5 mt), WA
recreational (43.2 mt), OR recreational (65 mt), and CA recreational
(116.7 mt) fisheries. In 2022, the trawl sector would receive 894.6 mt
of canary rockfish, of which 36 mt would be deducted to account for
bycatch in the at-sea sectors, and the remaining 858.6 mt would be
distributed to the shorebased IFQ sector. The non-trawl sector would
receive 343.1 mt, which is distributed to the commercial nontrawl
sector (123.5 mt), WA recreational (42.2 mt), OR recreational (63.5
mt), and CA recreational (113.9 mt) fisheries.
[GRAPHIC] [TIFF OMITTED] TP02OC20.008
[[Page 62503]]
Cowcod
For 2021-22, the Council recommended and NMFS is proposing setting
a cowcod ACT below the fishery harvest guideline at 50 mt, and having
it function as a fishery harvest guideline similar to the ACT in the
2017-18 and 2019-20 bienniums. The ACT would be allocated across
groundfish fisheries. Table 9 shows the trawl/nontrawl allocations for
cowcod for 2021 and 2022. NMFS anticipates the proposed allocation
structure will keep catch below the 2021-22 cowcod ACT. The ACT is
distributed to the trawl and non-trawl sectors, with the trawl sector
receiving 36 percent and the non-trawl sector receiving 64 percent each
year. In 2021 and 2022, the trawl sector would receive 18 mt of cowcod.
The non-trawl sector would receive 32 mt, which is distributed to the
commercial and recreational sectors as a 50/50 split.
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Lingcod South of 40[deg]10' N Lat.
The Council recommended and NMFS is proposing the trawl/nontrawl
allocations for lingcod south of 40[deg]10' N lat. in Table 10. These
allocations are anticipated to accommodate estimates of mortality of
lingcod, by sector, in 2021-22. Specifications of lingcod south of
40[deg]10' N lat. were established through Amendment 21 with a trawl/
non-trawl allocation set at 45 percent to trawl and 55 percent to non-
trawl. For the 2021-22 biennium, the Council recommended revising the
fixed percentages through Amendment 29 to the PCGFMP to better align
with current catch levels and provide some relief to the nontrawl
sector which is usually constrained by lingcod south of 40[deg]10' N
lat. Therefore, beginning with the 2021-22 biennium, the Council
recommended and NMFS is proposing changing trawl/non-trawl allocations
of lingcod south of 40[deg]10' N lat., so that 40 percent of the
harvest guideline for lingcod south of 40[deg]10' N lat. is allocated
to the trawl sector and 60 percent is allocated to the nontrawl sector.
In 2021, the distribution results in 435.6 mt to the trawl sector and
653.4 mt to the non-trawl sectors. In 2022, the distribution results in
463.6 mt to the trawl sectors and 695.4 mt to the non-trawl sectors. No
further allocations or distributions are made. The NOA for Amendment 29
is available for public comment (see ADDRESSES).
[GRAPHIC] [TIFF OMITTED] TP02OC20.010
Longnose Skate
The Council recommended and NMFS is proposing the trawl/nontrawl
allocations for longnose skate in Table 11. The allocation percentages,
90 percent to trawl and 10 percent to nontrawl, reflect historical
catch of longnose skate in the two sectors. These allocations are
anticipated to accommodate estimates of mortality of longnose skate
rockfish, by sector, in 2021-22. In 2021, the 90/10 distribution
results in 1,414.4 mt to the trawl sectors and 157.2 mt to the non-
trawl sectors. In 2022, the distribution results in 1,358.6 mt to the
trawl sectors and 151 mt to the non-trawl sectors.
[GRAPHIC] [TIFF OMITTED] TP02OC20.011
Minor Shelf Rockfish
Allocations for Minor Shelf Rockfish are recommended by the Council
and proposed by NMFS for each biennial cycle. The proposed allocations
for 2021 and 2022 are shown in Table 12. Specifications for the shelf
rockfish complex north of 40[deg]10' N lat. were established through
the biennial process with a trawl/non-trawl allocation for the 2021-22
specifications of 60.2 percent to trawl sectors and 39.8 percent to
non-trawl sectors. In 2021, the distribution results in 864.2 mt to the
trawl sectors and 571.4 mt to the non-trawl sectors. In 2022, the
distribution results in 827.5 mt to the trawl sectors and 547.1 mt to
[[Page 62504]]
the non-trawl sectors. Of the amount going to the trawl sectors, 35 mt
is deducted each year from the trawl allocation to account for bycatch
in the at-sea whiting sectors, with the remaining 829.2 mt in 2021 and
792.49 mt in 2022 going to the shorebased IFQ fishery. No further
allocations or distributions are made.
Specifications for the shelf rockfish complex south of 40[deg]10' N
lat. were established through the biennial process with a trawl/non-
trawl allocation for the 2021-22 specifications of 12.2 percent to
trawl sectors and 87.8 percent to non-trawl sectors. In 2021, the
distribution results in 161.7 mt to the trawl sectors and 1,163.6 mt to
the non-trawl sectors. In 2022, the distribution results in 160.5 mt to
the trawl sectors and 1,154.8 mt to the non-trawl sectors. No further
allocations or distributes are made.
[GRAPHIC] [TIFF OMITTED] TP02OC20.012
Slope Rockfish Complex
The slope rockfish complex south of 40[deg]10' N lat. is a fixed
allocation with a trawl/non-trawl allocation of 63 percent to trawl and
37 percent to non-trawl. For the 2021-22 biennium, the Council
recommended the fixed allocation be revised through Amendment 29 to the
PCGFMP and made into a 2-year allocation, with custom shares for
blackgill rockfish, to be reviewed each biennium. In 2021, the
distribution results in 556.9 mt to the trawl sectors and 152.1 mt to
the non-trawl sectors. In 2022, the distribution results in 515.6 mt to
the trawl sectors and 142.1 mt to the non-trawl sectors. The NOA for
Amendment 29 is open for public comment (see ADDRESSES).
[GRAPHIC] [TIFF OMITTED] TP02OC20.013
Petrale Sole
The Council recommended and NMFS is proposing the trawl/nontrawl
allocations for Petrale sole in Table 14. These allocations are
anticipated to accommodate estimates of mortality of Petrale sole, by
sector, in 2021-22. Petrale sole has a fixed allocation with a trawl/
non-trawl allocation of the fishery harvest guideline of 95 percent to
the trawl fishery and 5 percent to the non-trawl fishery. As part of
the 2021-22 biennium, the Council recommended changing the fixed
allocation to a biennial allocation through Amendment 29 to the PCGFMP
and revising the percentages to better align with current catch by
sector. Therefore, beginning in 2021, specifications for Petrale sole
will be determined as part of the biennial specifications process. For
the 2021-22 biennium, 30 mt of Petrale sole will be allocated to the
nontrawl sector and the remainder will go to the trawl sector each
year. This would shift around 150 and 130 mt to the shorebased IFQ
sector in 2021 and 2022, respectively, and would not constrain the
nontrawl sector. In 2021, the distribution results in 3,697.9 mt to the
trawl sector. In 2022, the trawl sector would receive 3,242.5 mt. The
NOA for Amendment 29 is open for public comment (see ADDRESSES).
[[Page 62505]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.014
Widow Rockfish
The Council recommended and NMFS is proposing the trawl/nontrawl
allocations for Widow rockfish in Table 15. These allocations are
anticipated to accommodate estimates of mortality of widow rockfish, by
sector, in 2021-22. Widow rockfish is an Amendment 21 species with a
trawl/non-trawl allocation of the fishery harvest guideline of 91
percent to the trawl fishery and 9 percent to the non-trawl fishery. As
part of the 2021-22 biennium, and through Amendment 29 to the PCGFMP,
the Council recommended making it a biennial allocation and providing a
fixed amount to the nontrawl sector to better align with current catch
by sector. Therefore, beginning in 2021, specifications for widow
rockfish will be determined as part of the biennial specifications
process. For the 2021-22 biennium, 400 mt of widow rockfish will be
allocated to the nontrawl sector and the remainder will go to the trawl
sector each year. This would shift just under 1,000 mt of widow
rockfish to the shorebased IFQ sector in 2021 and 2022, and would not
constrain the nontrawl sector. In 2021, the distribution results in
14,076.7 mt to the trawl sector. In 2022, the trawl sector would
receive 13,139.7 mt. The NOA for Amendment 29 is open for public
comment (see ADDRESSES).
[GRAPHIC] [TIFF OMITTED] TP02OC20.015
D. Corrections to Waypoints for Rockfish Conservation Areas
Rockfish Conservation Areas (RCAs) are large area closures intended
to reduce the catch of a stock or stock complex by restricting fishing
activity at specific depths. The boundaries for RCAs are defined by
straight lines connecting a series of latitude and longitude
coordinates that approximate depth contours. These sets of coordinates,
or lines, are not gear or fishery specific, but can be used in
combination to define an area. NMFS then implements fishing
restrictions for a specific gear and/or fishery within each defined
area.
For the 2021-22 biennium, the Council recommended and NMFS is
proposing minor adjustments to the 40 fathom (fm) depth contour
offshore of San Mateo in Central California, and the 100 fm depth
contours off of California to more accurately refine the depth
contours, as well as the addition of a 100 fm line around the Channel
Islands. See Chapter 2 of the Analysis for more details on these
changes.
E. Limited Entry Trawl
The limited entry trawl fishery is made up of the shorebased IFQ
program, whiting and non-whiting, and the at-sea whiting sectors. For
some stocks and stock complexes with a trawl allocation, an amount is
first set-aside for the at-sea whiting sector with the remainder of the
trawl allocation going to the shorebased IFQ sector. Set-asides are not
managed by NMFS or the Council except in the case of a risk to the ACL.
At-Sea Set Asides
For several species, the trawl allocation is reduced by an amount
set-aside for the at-sea whiting sector. This amount is designed to
accommodate catch by the at-sea whiting sector when they are targeting
Pacific whiting. The Council considered several proposals to generate
amounts for these set-asides. After much discussion and analysis, the
Council is recommending and NMFS is proposing the set-asides in Table
16 for the 2021-22 biennium.
[[Page 62506]]
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Incidental Trip Limits for IFQ Vessels
For vessels fishing in the Shorebased IFQ Program, with either
groundfish trawl gear or nontrawl gears, the following incidentally-
caught stocks are managed with trip limits: Minor Nearshore Rockfish
north and south, black rockfish, cabezon (46[deg]16' to 40[deg]10' N
lat. and south of 40[deg]10' N lat.), spiny dogfish, shortbelly
rockfish, big skate, Pacific whiting, and the Other Fish complex. For
all these stocks except big skate, this rule proposes maintaining the
same IFQ fishery trip limits for these stocks for the start of the
2021-22 biennium as those in place in 2019. For big skate, the Council
proposes an unlimited trip limit to start the 2021 fishing year.
Additionally, the Council is recommending and NMFS is proposing a trip
limit for blackgill rockfish within the southern slope rockfish
complex. The trip limit would be unlimited to start the 2021 fishing
year. The purpose of the blackgill trip limit would be to allow the
Council to reduce targeting of blackgill rockfish inseason, if needed.
Trip limits for the IFQ fishery can be found in Table 1 North and Table
1 South to part 660, subpart D, in the regulatory text of this proposed
rule. Changes to trip limits would be considered a routine measure
under Sec. 660.60(c), and may be implemented or adjusted, if
determined necessary, through inseason action.
F. LEFG and OA Nontrawl Fishery
Management measures for the LEFG and OA nontrawl fisheries tend to
be similar because the majority of participants in both fisheries use
hook-and-line gear. Management measures, including area restrictions
(e.g., nontrawl RCA) and trip limits in these nontrawl fisheries, are
generally designed to allow harvest of target stocks while keeping
catch of overfished stocks low. For the 2021-22 biennium, the Council
considered increasing trip limits for almost all LEFG and OA fisheries,
many of which are decades old and do not reflect stocks rebuilding in
previous biennium and management changes (e.g., stock complex
reorganizations). LEFG and OA trip limits are specified in Table 2
(North), Table 2 (South) to subpart E for LEFG and in Table 3 (North)
and Table 3 (South) to subpart F for OA in the regulatory text of this
proposed rule.
Sablefish Trip Limits
Sablefish are managed separately north and south of 36[deg] N lat.
For the portion of the stock north of 36[deg] N lat., the Council
recommended and NMFS is proposing higher trip limits for the LEFG and
OA fisheries in 2021. For the portion south of 36[deg] N lat., the
Council recommended removing the daily trip limit for the OA fishery
but maintaining the same weekly and bimonthly trip limits as were in
place in the start of 2019. The proposed sablefish trip limits for
2021-22 are shown in Table 17.
[[Page 62507]]
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LEFG and OA Trip Limits
The Council recommended, and NMFS is proposing higher trip limits
for LEFG and OA fisheries in 2021, including trip limits for shortspine
thornyhead, longspine thornyhead, widow rockfish, shelf rockfish,
shortbelly rockfish, canary rockfish, Pacific ocean perch, yellowtail
rockfish, slope rockfish, darkblotched rockfish, Lingcod, nearshore
rockfish, black rockfish, Other Flatfish, bocaccio south of 40[deg]10'
N lat., and chilipepper rockfish (Agenda Item G.6.a., Supplemental GMT
Report 2, April 2020). These increases in trip limits are meant to help
members of industry harvest more fish while still keeping total
mortality within the ACLs for these stocks and stock complexes. Further
information on these trip limits can be found in Section 4.3.5.1 of the
Analysis.
As part of the Council's recommended trip limits for the LEFG and
OA fisheries, the Council established an OA trip limit for shortspine
and longspine thornyheads in the area between 40[deg]10' N lat. and
34[deg]27' N lat. As part of the Council's action during the 2019-20
biennium, the Council recommended and NMFS implemented, trip limits for
OA fisheries for shortspine and longspine thornyheads north of
40[deg]10' N. lat. and south of 34[deg]27' N lat., but inadvertently
omitted the trip limit for the area between 40[deg]10' N lat. and
34[deg]27' N lat., leaving this area closed. The Council is
recommending, and NMFS is proposing, implementing a 50 lb (22.7 kg) per
month limit for OA fisheries targeting shortspine and longspine
thornyheads in the area between 40[deg]10' N lat. and 34[deg]27' N lat.
This is the same trip limit currently proposed for OA fisheries
targeting shortspine and longspine thornyheads north of 40[deg]10' N
lat. See Section 4.5.6.1 of the Analysis for more information on this
change.
Primary Sablefish Tier Limits
Some limited entry fixed gear permits are endorsed to receive
annual sablefish quota, or tier limits. Vessels registered with one,
two, or up to three of these permits may participate in the primary
sablefish fishery. The proposed tier limits are as follows: In 2021,
Tier 1 at 58,649 lb (26,602 kg), Tier 2 at 26,659 lb (12,092 kg), and
Tier 3 at 15,234 lb (6,910 kg). For 2022, Tier 1 at 55,858 lb (25,337
kg), Tier 2 at 25,390 lb (11,517 kg), and Tier 3 at 14,509 lb (6,581
kg).
Yellowtail Trip Limit for the Salmon Troll Fishery North of 40[deg]10'
N lat.
During public comment at the November 2019 Council meeting, there
was a request to increase the yellowtail rockfish ratio and monthly
limits in the salmon troll fishery north of 40[deg]10' N lat. The
current ratio and limit are 1lb (0.45 kg) of yelloweye rockfish for
every 2 lb (0.9 kg) of salmon landed, with a 200 lb (91 kg) monthly
limit. As part of the 2017-18 biennial cycle, yellowtail rockfish was
removed from the OA multi-stock trip limit, and a new separate trip
limit of 500 lb (227 kg) per month was recommended by the Council and
implemented by NMFS; however, the salmon troll yellowtail rockfish trip
limit did not reflect this change. Agenda Item G.6., Attachment 3
(April 2019) contains a detailed analysis of the salmon troll trip
limits considered by the Council. After consideration of the detailed
analysis, the Council recommended and NMFS is proposing increasing the
yellowtail rockfish limit in the salmon troll fishery north of
40[deg]10' N lat. from 200 lbs (91 kg) to 500 lbs (227 kg) and removing
the ratio for yellowtail to salmon.
Removal of Other Flatfish Gear Restriction Off California
Currently, Federal regulations in Table 2 (South) to Part 660,
Subpart E and Table 3 (South) to Part 660, Subpart F include a gear
restriction for vessels targeting stocks in the Other Flatfish complex
south of 42[deg] N lat. while inside the boundaries of the nontrawl
RCA. The gear restriction limits the number of hooks per line, size of
the hooks, and the number and size of the weights. Other flatfish
include butter sole, curlfin sole, Pacific sanddab, rex sole, rock
sole, and sand sole, as defined in 50 CFR 660.11. This management
measure was originally implemented in 2003 to protect bocaccio, which
was overfished at that time and was thought to provide protections to
other overfished groundfish stocks in following years (e.g., Petrale
sole) while still allowing an artisanal sanddab fishery off California.
However, it was determined in subsequent cycles that it was not
effective at preventing bycatch of overfished species. During the 2009-
10 harvest specifications cycle, this restriction was removed from
regulations for the recreational fishery but was kept for the
commercial fishery.
Since this measure was first implemented the stocks it was intended
to protect have all been rebuilt while the Other Flatfish complex
continues to be under-attained. Therefore, to provide more opportunity
to target stocks in the Other Flatfish complex, the Council recommended
and NMFS is proposing removing the gear restrictions for the LEFG and
OA fisheries targeting stocks in the Other Flatfish complex inside the
RCA south of 42[deg] N lat.
[[Page 62508]]
Nontrawl RCA Adjustments
Increasing the LEFG and OA trip limits, as proposed in Section III,
F., LEFG and OA Fishery, of this proposed rule is one way to help
increase attainment of many currently under-attained species. However,
as has been discussed under public comment at Council meetings during
development of this action, increasing trip limits without providing
access to the areas where those fish can be found does little to help
with attainments. Therefore, as part of the 2021-22 biennium, the
Council recommended and NMFS is proposing the following changes to the
Nontrawl RCA off Oregon and Washington:
Between 40[deg]10' N lat. and 46[deg]16' N lat. (the
Oregon-Washington border): Open the area between the 30- and 40-fm
management lines to hook-and-line gear except bottom longline and
dinglebar, as defined in the ``general definitions'' section of the
Federal regulations at 50 CFR 660.11;
Between 38[deg]57.5' N lat. and 34[deg]27' N lat., (Point
Arena to Point Conception): Open the area between 40 fm and 50 fm; and
South of 34[deg]27' N lat.: Open the area between 75 fm
and 100 fm.
These proposals, along with the proposed changes to recreational
conservation areas (discussed in Section III, H., Recreational
Fisheries) will provide much needed access to these areas for the LEFG
and OA fisheries to better attain their trip limits. Section 4.7.2 of
the Analysis provides a detailed assessment of the impacts of these
openings. Nontrawl RCA closures can be found in the LEFG and OA trip
limits in Table 2 (North), Table 2 (South) to subpart E for LEFG and in
Table 3 (North) and Table 3 (South) to subpart F for OA in the proposed
regulatory text of this proposed rule.
As provided in the Analysis, the purpose of opening these areas is
to provide LEFG and OA fisheries access to areas where they can catch
abundant target stocks, such as bocaccio, canary rockfish, yellowtail
rockfish, and widow rockfish. All of these stocks have been
underutilized by the LEFG and OA fisheries since they were rebuilt due
to limited access to the areas where they can be found. Opening these
areas of the nontrawl RCA, many of which are currently already open to
other types of fishing (i.e., trawl or recreational fishing with hook
and line gear), along with the increased LEFG and OA trip limits for
many of these stocks and stock complexes will likely result in greater
attainment of the nontrawl allocations and therefore the ACLs without
increasing the risks of exceeding these limits.
New Management Line at 38[deg]57.5' N lat.
In order to make some of the proposed changes to the Nontrawl RCA,
the Council also recommended and NMFS is proposing creating a new
management line at 38[deg]57.5' N lat., which is Point Arena,
California. Point Arena is already defined in Federal regulations under
the definition for North-South Management Areas, as a commonly used
geographic coordinate.
H. Recreational Fisheries
This section describes the recreational fisheries management
measures proposed for 2021-22. The Council primarily recommends depth
restrictions and groundfish conservation areas to constrain catch
within the recreational harvest guidelines for each stock. Washington,
Oregon, and California each proposed, and the Council recommended,
different combinations of seasons, bag limits, area closures, and size
limits for stocks targeted in recreational fisheries. These measures
are designed to limit catch of overfished stocks found in the waters
adjacent to each state while allowing target fishing opportunities in
their particular recreational fisheries. The following sections
describe the recreational management measures proposed in each state.
Washington
The state of Washington manages its marine fisheries in four areas:
Marine Area 1 extends from the Oregon/Washington border to Leadbetter
Point; Marine Area 2 extends from Leadbetter Point to the mouth of the
Queets Rivers; Marine Area 3 extends from the Queets River to Cape
Alava; and Marine Area 4 extends from Cape Alava to the Sekiu River.
This proposed rule would adopt the following season structure in Table
18.
[GRAPHIC] [TIFF OMITTED] TP02OC20.018
[[Page 62509]]
The aggregate groundfish bag limits in waters adjacent to
Washington would continue to be nine fish in all areas with a sub-bag
limit for cabezon (one per day), rockfish (seven per day), and lingcod
(two per day). The flatfish limit would increase from three fish to
five fish, and is not counted towards the groundfish bag limit of nine
but is in addition to it. The Council recommended these season and bag
limit changes, which allow more access to target stocks with fewer
restrictions.
Consistent with the 2019-20 biennium, the Council recommended and
NMFS is proposing to continue to prohibit recreational fishing for
groundfish and Pacific halibut inside the North Coast Recreational
Yelloweye Rockfish Conservation Area (YRCA), a C-shaped closed area off
the northern Washington coast. However, the Council recommended and
NMFS is proposing opening the South Coast Recreational YRCA and the
Westport Offshore YRCA to recreational fishing for the 2021-22
biennium. Coordinates for YRCAs are defined at Sec. 660.70.
Opening the South Coast Recreational YRCA and the Westport Offshore
YRCA would provide additional access to healthy underutilized stocks.
Originally closed to recreational fishing in 2007 to protect canary
rockfish and yelloweye rockfish, these closures may no longer be needed
since canary rockfish has been rebuilt and higher harvest guidelines
were implemented for yelloweye rockfish. As stated by the Washington
Department of Fish and Wildlife (WDFW) in their analysis for this
proposal, the additional impacts to target and non-target species
expected from allowing recreational hook-and-line fishing in these
areas would be minimal because the areas to be opened are very small,
particularly in comparison to the overall area used by Washington
recreational fisheries (Agenda Item F.1.a, Supplemental WDFW Report 1,
June 2020).
Oregon
The Council proposed that Oregon recreational fisheries in 2021-22
would operate under an all months all depths season structure to start
the 2021 fishing year. The Council proposed maintaining the 2019-20
aggregate bag limits and size limits in Oregon recreational fisheries
for 2021-22. The proposed limits are: Three lingcod per day, with a
minimum size of 22 in (56 cm); 25 flatfish per day, excluding Pacific
halibut; and a marine fish aggregate bag limit of 10 fish per day,
where cabezon have a minimum size of 16 in (41 cm).
The ODFW also requested that the Council consider allowing
longleader gear fishing and ``all-depth'' Pacific halibut fishing on
the same trip, which had been requested by Oregon anglers during
discussion of the 2019 Pacific halibut Catch Sharing Plan process.
Currently, combining the two trip types is prohibited; this prohibition
was meant to limit interactions with yelloweye rockfish.
Impacts to yelloweye rockfish or other species of concern (e.g.,
Chinook and Coho salmon) are unlikely to increase significantly under
this proposed change as effort is not expected to increase by much.
Instead, removing the prohibition would allow anglers already
participating in one or the other fisheries to have additional
opportunity while offshore. As ODFW's analysis to the Council shows
(Agenda Item F.1.a, June 2020), over the past 2 years that the
longleader gear fishery has been allowed to operate, the average
encounter rates of yelloweye rockfish, Chinook salmon, and Coho salmon
has been extremely low at around 0.02, 0.6, and 6 fish per angler,
respectively. When added to the encounters from the traditional
bottomfish fishery, the total annual encounters would not be much
different than the recent years' total estimates, and should not
increase the potential for the total groundfish salmon thresholds to be
reached or exceeded. Therefore the Council recommended and NMFS is
proposing removing the prohibition on combining Oregon longleader trips
with all depths halibut trips.
California
The Council manages recreational fisheries in waters adjacent to
California in five separate management areas. Season and area closures
differ between California management areas to limit incidental catch of
overfished stocks while providing as much recreational fishing
opportunity as possible. The Council's proposed California season
structure includes additional time and depth opportunities, which are
supported by the proposed increase to the yelloweye rockfish ACL
described in Section C. Table 19 shows the proposed season structure
and depth limits by management area for 2021 and 2022.
[GRAPHIC] [TIFF OMITTED] TP02OC20.019
[[Page 62510]]
The Council recommended that size limits would remain the same as
for 2020 for all stocks. However, the Council recommended and NMFS is
proposing to eliminate the sub-bag limits for black rockfish, canary
rockfish, and cabezon, and establish a sub-bag limit for vermillion
rockfish of five fish.
J. Exempted Fishing Permits
This action is authorized by the PCGFMP and the regulations
implementing the Magnuson-Stevens Act at 50 CFR 600.745, which state
that EFPs may be used to authorize fishing activities that would
otherwise be prohibited.
At its June 2020 meeting, the Council recommended that NMFS approve
five EFP applications for the 2021 fishing year and preliminarily
approve the EFP applications for the 2022 fishing year. The Council
considered these EFP applications concurrently with the 2021-2022
biennial harvest specifications and management process because expected
catch under most EFP projects is included in the catch limits for
groundfish stocks. Three of the EFP applications are renewals, and
request to test hook-and-line gear that selectively targets
underutilized, midwater rockfish species (e.g., yellowtail rockfish)
while avoiding overfished, bottom-dwelling rockfish species (e.g.,
yelloweye rockfish). An EFP is necessary for these activities because
they will all occur in the non-trawl RCA, which is closed to fishing
with non-trawl fixed gear to protect overfished groundfish stocks. The
other two EFP applications are new, and request to retain certain
prohibited species in order to collect fishery-dependent data for
potential use in upcoming stock assessments. A summary of each EFP
application is provided below:
Groundfish EFP Proposal--Yellowtail Rockfish Jig Fishing
off California: The San Francisco Community Fishing Association (SFCFA)
and private open access fisherman Daniel Platt submitted a renewal
application for research that has been conducted since 2013. The
purpose of the EFP project is to continue testing the potential for a
commercial jig gear configured to target underutilized, midwater
yellowtail and shelf rockfish species while avoiding the rebuilding,
bottom-dwelling yelloweye rockfish. The EFP project would require
exemptions from: (1) The prohibition to fish inside the non-trawl RCA
with non-trawl gear (see Sec. 660.330(d)(12)(i)); (2) the prohibition
on transiting through the non-trawl RCA without non-trawl gear stowed
(see Sec. 660.330(d)(12)(ii)); and (3) the prohibition on retaining
and landing groundfish harvested from inside the non-trawl RCA with
non-trawl gear (see Sec. 660.330(d)(12)(iii)). If approved, NMFS would
authorize up to seven vessels to target midwater rockfish inside the
non-trawl RCA off the California coast--specifically between 40[deg]
10' north latitude (N lat.) and Point Conception, California, at depths
ranging from 35 to 150 fathoms (64 to 274 meters (m)).
Groundfish EFP Proposal--Commercial Midwater Hook-and-Line
Rockfish Fishing in the RCA off the Oregon Coast: Scott Cook, a private
fisherman of Coos Bay, Oregon submitted a renewal application to
continue research that has been conducted since 2019. The purpose of
the EFP project is to test a modified, midwater trolled longline gear
configured to target underutilized, midwater yellowtail, widow, and
canary rockfish, while avoiding the rebuilding, bottom-dwelling
yelloweye rockfish. The EFP project would require exemptions from: (1)
The prohibition to fish inside the non-trawl RCA with non-trawl gear
(see Sec. 660.330(d)(12)(i)); (2) the prohibition on transiting
through the non-trawl RCA without non-trawl gear stowed (see Sec.
660.330(d)(12)(ii)); and (3) the prohibition on retaining and landing
groundfish harvested from inside the non-trawl RCA with non-trawl gear
(see Sec. 660.330(d)(12)(iii)). If approved, NMFS would authorize up
to five vessels to target midwater rockfish inside the non-trawl RCA
off the Oregon Coast--specifically in the rocky reef habitat at depths
ranging from 30 to 100 fathoms (55 to 183 m).
Groundfish EFP Proposal--Monterey Bay Regional EFP
Chilipepper Rockfish: Real Good Fish of Moss Landing, California
submitted a renewal application to continue research that has been
conducted since 2019. The purpose of the EFP project is to test a
trolled hook-and-line gear configured to target underutilized, midwater
chilipepper rockfish and avoid the rebuilding, bottom-dwelling
yelloweye rockfish. The EFP project would require exemptions from: (1)
The prohibition to fish inside the non-trawl RCA with non-trawl gear
(see Sec. 660.330(d)(12)(i)); (2) the prohibition on transiting
through the non-trawl RCA without non-trawl gear stowed (see Sec.
660.330(d)(12)(ii)); and (3) the prohibition on retaining and landing
groundfish harvested from inside the non-trawl RCA with non-trawl gear
(see Sec. 660.330(d)(12)(iii)). If approved, NMFS would authorize up
to 10 vessels to target midwater rockfish inside the non-trawl RCA off
the California coast--specifically in areas with canyon edges and walls
that have historically produced high volumes of chilipepper rockfish
catch and at depths ranging from 40 to 150 fathoms (73 to 274 m).
Groundfish EFP Proposal--California Department of Fish and
Wildlife 2021-2022 EFP: The California Department of Fish and Wildlife
(CDFW) submitted a new EFP application to collect fishery-dependent
biological data for cowcod for inclusion in future stock assessments.
The EFP project would require an exemption from the prohibition to
retain cowcod in the California recreational fishery (see Sec.
660.360(c)(3)). The EFP would also provide that any cowcod taken and
retained would not count against the recreational bag limit for the
aggregate of rockfish, cabezon, and greenlings. If approved, NMFS would
authorize up to 20 vessels that participate in the California
recreational fishery to retain cowcod and transfer the cowcod to CDFW
groundfish staff upon landing.
Groundfish EFP Proposal--Washington Department of Fish
Wildlife Enhanced Yelloweye Recreational Fishery Biological Sampling
EFP: The Washington Department of Fish and Wildlife (WDFW) submitted a
new EFP application to collect fishery-dependent biological data for
yelloweye rockfish for inclusion in future stock assessments. The EFP
project would require an exemption from the prohibition to retain
yelloweye rockfish in the Washington recreational fishery (see Sec.
660.360(c)(1)(ii)). The EFP would also provide that any yelloweye
rockfish taken and retained would not count against the recreational
bag limit for rockfish. If approved, NMFS would authorize up to 10
vessels that participate in the Washington recreational fishery to
retain yelloweye rockfish and transfer the yelloweye rockfish to WDFW
staff upon landing.
During the 2-year period of EFP activities from 2021 to 2022, all
vessels participating in the non-trawl RCA EFP projects (i.e., the
renewal applications submitted by the SFCFA, Scott Cook, and Real Good
Fish) would adhere to EFP set-asides for targeted and incidental
groundfish and other species, which were considered and approved by the
Council at their June 2020 meeting. These EFP set-asides are off-the-
top deductions from the 2021-2022 applicable ACLs, meaning any landings
and discards that occur under these EFPs would be accounted for within
the applicable ACLs. These vessels are also required to have 100
percent observer coverage. All cowcod mortality under the CDFW EFP
project is expected to
[[Page 62511]]
occur in conjunction with routine recreational fishing activities and
will be calculated as part of the normal recreational catch estimation
process. All yelloweye rockfish taken under the WDFW EFP project would
be counted against the Washington recreational harvest guideline for
yelloweye rockfish. NMFS would not require 100 percent observer
coverage for vessels participating in the CDFW and WDFW EFP projects
because recreational vessels do not meet the minimum size requirements
under Federal regulations to carry an observer.
NMFS does not expect any impacts to the environment, essential fish
habitat, or protected or prohibited species from these EFPs beyond
those analyzed for the groundfish fishery as a whole in applicable
biological opinions 3 4 or the draft Environmental
Assessment (EA) for the Pacific Coast Groundfish Fishery 2021-2022
Harvest Specifications and Management Measures.\5\
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\3\ Available at: https://www.westcoast.fisheries.noaa.gov/publications/fishery_management/groundfish/s7-groundfish-biop-121117.pdf.
\4\ Available at: https://www.pcouncil.org/wp-content/uploads/2017/10/F7_Att1_USFWS_2017_STALBiOp_NOV2017BB.pdf.
\5\ Draft available at: https://www.pcouncil.org/documents/2020/05/f-1-attachment-8-pacific-coast-groundfish-fishery-2021-2022-harvest-specifications-and-management-measures-analytical-document-organized-as-a-draft-environmental-assessment-chapters-1-5-electroni.pdf/.
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After publication of this document in the Federal Register, NMFS
may approve and issue permits for the proposed EFP projects for the
2021 fishing year after the close of the public comment period. All
five EFP applications are available under ``Supporting and Related
Materials'' (see ADDRESSES). NMFS will consider comments submitted in
deciding whether to approve the applications as requested. NMFS may
approve the applications in their entirety or may make any alterations
needed to achieve the goals of the EFP projects. NMFS would not issue
another Federal Register notice soliciting public comment on renewing
these EFP projects for 2022 unless: (1) The applicants modify and
resubmit their applications to NMFS; (2) changes to relevant fisheries
regulations warrant a revised set of exemptions authorized under the
EFP projects; or (3) NMFS' understanding of the current biological and
economic impacts from EFP fishing activities substantially changes.
IV. Classification
Pursuant to section 304(b)(1)(A) of the Magnuson-Stevens Act, the
NMFS Assistant Administrator has determined that this proposed rule is
consistent with the PCGFMP, 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 PCGFMP. 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 PCGFMP establish a procedure by
which the tribes with treaty fishing rights in the area covered by the
PCGFMP request new allocations or regulations specific to the tribes,
in writing, before the first of the two meetings at which the Council
considers groundfish management measures. The regulations at 50 CFR
660.324(d) further direct NMFS to develop tribal allocations and
regulations in consultation with the affected tribes. The tribal
management measures in this proposed rule have been developed following
these procedures. The tribal representative on the Council made a
motion to adopt the non-whiting tribal management measures, which was
passed by the Council. Those management measures, which were developed
and proposed by the tribes, are included in this proposed rule.
This proposed rule has been determined to be 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.
NMFS prepared an integrated Analysis for this action, which
addresses the statutory requirements of the Magnuson-Stevens Act, the
National Environmental Policy Act, Presidential Executive Order 12866,
and the Regulatory Flexibility Act. 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 an EIS was prepared for the 2015-16 biennial harvest
specifications and management measures and is available from NMFS (see
ADDRESSES). This EIS 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 2021-22 cycle tiers from the
2015-16 EIS and focuses on the harvest specifications and management
measures that were not within the scope of the 10-year projections in
the 2015-16 EIS. A copy of the EA is available from NMFS (see
ADDRESSES). This action also announces a public comment period on the
EA.
The Chief Counsel for Regulation of the Department of Commerce
certified to the Chief Counsel for Advocacy of the Small Business
Administration that this proposed rule, if adopted, would not have a
significant economic impact on a substantial number of small entities.
The purpose of this proposed rule is to conserve Pacific Coast
groundfish stocks by preventing overfishing, while still allowing
harvest opportunity among the various fishery sectors. This will be
accomplished by implementing the 2021-2022 annual specifications in the
U.S. exclusive economic zone off the West Coast. The harvest
specifications affect large and small entities similarly, and for this
biennium, many of the catch limits are proposed to increase, providing
benefit to all participants. Additionally, this proposed rule contains
several of new management measures that are likely to benefit vessels,
specifically openings of previously closed fishing grounds. As a
result, an initial regulatory flexibility analysis is not required and
none has been prepared.
List of Subjects in 50 CFR Part 660
Fisheries, Fishing, Reporting and recordkeeping requirements.
Dated: September 28, 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.
[[Page 62512]]
0
2. In Sec. 660.11, amend the definition of ``North-South management
area'' by revising paragraph (2)(xviii) to read as follows:
Sec. 660.11 General definitions.
* * * * *
North-South management area * * *
(2) * * *
(xviii) Point Arena, CA--management line--38[deg]57.50' N lat.
* * * * *
0
3. In Sec. 660.40, revise the section heading, removing paragraph (a),
redesignating paragraph (b) as paragraph (a), and add a reserved
paragraph (b) to read as follows:
Sec. 660.40 Rebuilding plans.
* * * * *
0
4. In Sec. 660.50, revise paragraphs (f)(2)(ii) and (f)(6) to read as
follows:
Sec. 660.50 Pacific Coast treaty Indian fisheries.
* * * * *
(f) * * *
(2) * * *
(ii) The Tribal allocation is 689.2 mt in 2021 and 656.6 mt in 2022
per year. This allocation is, for each year, 10 percent of the Monterey
through Vancouver area (North of 36[deg] N lat.) ACL. The Tribal
allocation is reduced by 1.7 percent for estimated discard mortality.
* * * * *
(6) Petrale sole. For petrale sole, treaty fishing vessels are
restricted to a fleetwide harvest target of 350 mt each year.
* * * * *
0
5. Amend Sec. 660.71 as follows:
0
a. Redesignate paragraphs (o)(133) through (216) as paragraphs (o)(135)
through (218); and
0
b. Add new paragraphs (o)(133) and (134).
The additions read as follows:
Sec. 660.71 Latitude/longitude coordinates defining the 10-fm (18-m)
through 40-fm (73-m) depth contours.
* * * * *
(o) * * *
(133) 37[deg]25.00' N lat., 122[deg]38.66' W long.;
(134) 37[deg]20.68' N lat., 122[deg]36.79' W long.;
* * * * *
0
6. Amend Sec. 660.73 as follows:
0
a. Revise paragraphs (a)(309) through (315);
0
b. Add paragraphs (a)(316) through (321);
0
c. Revise paragraphs (b)(1) through (14);
0
d. Add paragraph (b)(15);
0
e. Revise paragraphs (c)(10) through (14);
0
f. Redesignate paragraphs (d) through (l) as paragraphs (e) through
(m); and
0
g. Add new paragraph (d).
The revisions and additions read as follows:
Sec. 660.73 Latitude/longitude coordinates defining the 100 fm (183
m) through 150 fm (274 m) depth contours.
* * * * *
(a) * * *
(309) 33[deg]2.81' N lat., 117[deg]21.17' W long.;
(310) 33[deg]1.76' N lat., 117[deg]20.51' W long.;
(311) 32[deg]59.90' N lat., 117[deg]19.38' W long.;
(312) 32[deg]57.29' N lat., 117[deg]18.94' W long.;
(313) 32[deg]56.15' N lat., 117[deg]19.54' W long.;
(314) 32[deg]55.30' N lat., 117[deg]19.38' W long.;
(315) 32[deg]54.27' N lat., 117[deg]17.17' W long.;
(316) 32[deg]52.94' N lat., 117[deg]17.11' W long.;
(317) 32[deg]52.66' N lat., 117[deg]19.67' W long.;
(318) 32[deg]50.95' N lat., 117[deg]21.17' W long.;
(319) 32[deg]47.11' N lat., 117[deg]22.98' W long.;
(320) 32[deg]45.60' N lat., 117[deg]22.64' W long.; and
(321) 32[deg]42.79' N lat., 117[deg]21.16' W long.
(b) * * *
(1) 33[deg]04.80' N lat., 118[deg]37.90' W long.;
(2) 33[deg]02.65' N lat., 118[deg]34.08' W long.;
(3) 32[deg]55.80' N lat., 118[deg]28.92' W long.;
(4) 32[deg]55.04' N lat., 118[deg]27.68' W long.;
(5) 32[deg]49.79' N lat., 118[deg]20.87' W long.;
(6) 32[deg]48.05' N lat., 118[deg]19.62' W long.;
(7) 32[deg]47.41' N lat., 118[deg]21.86' W long.;
(8) 32[deg]44.03' N lat., 118[deg]24.70' W long.;
(9) 32[deg]47.81' N lat., 118[deg]30.20' W long.;
(10) 32[deg]49.79' N lat., 118[deg]32.00' W long.;
(11) 32[deg]53.36' N lat., 118[deg]33.23' W long.;
(12) 32[deg]55.13' N lat., 118[deg]35.31' W long.;
(13) 33[deg]00.22' N lat., 118[deg]38.68' W long.;
(14) 33[deg]03.13' N lat., 118[deg]39.59' W long.; and
(15) 33[deg]04.80' N lat., 118[deg]37.90' W long.
(c) * * *
(10) 33[deg]18.14' N lat., 118[deg]27.94' W long.;
(11) 33[deg]19.84' N lat., 118[deg]32.22' W long.;
(12) 33[deg]20.81' N lat., 118[deg]32.91' W long.;
(13) 33[deg]21.94' N lat., 118[deg]32.03' W long.;
(14) 33[deg]23.14' N lat., 118[deg]30.12' W long.;
* * * * *
(d) The 100 fm (183 m) depth contour around the northern Channel
Islands off the state of California is defined by straight lines
connecting all of the following points in the order stated:
(1) 34[deg]12.89' N lat., 120[deg]29.31' W long.;
(2) 34[deg]10.96' N lat., 120[deg]25.19' W long.;
(3) 34[deg]08.74' N lat., 120[deg]18.00' W long.;
(4) 34[deg]07.02' N lat., 120[deg]10.45' W long.;
(5) 34[deg]06.75' N lat., 120[deg]05.09' W long.;
(6) 34[deg]08.15' N lat., 119[deg]54.96' W long.;
(7) 34[deg]'07.17 N lat., 119[deg]48.54' W long.;
(8) 34[deg]05.66' N lat., 119[deg]37.58' W long.;
(9) 34[deg]04.76' N lat., 119[deg]26.28' W long.;
(10) 34[deg]02.93' N lat., 119[deg]18.06' W long.;
(11) 34[deg]00.97' N lat., 119[deg]18.78' W long.;
(12) 33[deg]59.38' N lat., 119[deg]21.71' W long.;
(13) 33[deg]58.62' N lat., 119[deg]32.05' W long.;
(14) 33[deg]57.69' N lat., 119[deg]33.38' W long.;
(15) 33[deg]57.40' N lat., 119[deg]35.84' W long.;
(16) 33[deg]56.07' N lat., 119[deg]41.10' W long.
(17) 33[deg]55.54' N lat., 119[deg]47.99' W long.;
(18) 33[deg]56.60' N lat., 119[deg]51.40' W long.;
(19) 33[deg]55.56' N lat., 119[deg]53.87' W long.;
(20) 33[deg]54.40' N lat., 119[deg]53.74' W long.;
(21) 33[deg]52.72' N lat., 119[deg]54.62' W long.;
(22) 33[deg]47.95' N lat., 119[deg]53.50' W long.;
(23) 33[deg]45.75' N lat., 119[deg]51.04' W long.;
(24) 33[deg]40.18' N lat., 119[deg]50.36' W long.;
(25) 33[deg]38.19' N lat., 119[deg]57.85' W long.;
(26) 33[deg]44.92' N lat., 120[deg]02.95' W long.;
[[Page 62513]]
(27) 33[deg]48.90' N lat., 120[deg]05.34' W long.;
(28) 33[deg]51.64' N lat., 120[deg]08.11' W long.;
(29) 33[deg]58.31' N lat., 120[deg]27.99' W long.;
(30) 34[deg]03.23' N lat., 120[deg]34.34' W long.;
(31) 34[deg]09.42' N lat., 120[deg]37.64' W long.; and
(32) 34[deg]12.89' N lat., 120[deg]29.31' W long.
* * * * *
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7. Tables 1a through 1c to subpart C are revised to read as follows:
[[Page 62514]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.020
[[Page 62515]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.021
[[Page 62516]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.022
[[Page 62517]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.023
[[Page 62518]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.024
[[Page 62519]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.025
[[Page 62520]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.026
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6. Tables 2a through 2c to subpart C are revised to read as follows:
[[Page 62521]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.027
[[Page 62522]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.028
[[Page 62523]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.029
[[Page 62524]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.030
[[Page 62525]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.031
[[Page 62526]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.032
[[Page 62527]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.033
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7. In Sec. 660.140, revise paragraphs (d)(1)(ii)(D) to read as
follows:
Sec. 660.140 Shorebased IFQ Program.
* * * * *
(d) * * *
(1) * * *
[[Page 62528]]
(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:
[GRAPHIC] [TIFF OMITTED] TP02OC20.034
[[Page 62529]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.035
* * * * *
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8. Revise Tables 1 (North) and 1 (South) to subpart D to read as
follows:
[[Page 62530]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.036
[[Page 62531]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.037
0
9. In Sec. 660.231, revise paragraph (b)(3)(i) to read as follows:
Sec. 660.231 Limited entry fixed gear sablefish primary fishery.
* * * * *
(b) * * *
(3) * * *
(i) A vessel participating in the primary season will be
constrained by the sablefish cumulative limit associated with each of
the permits registered for use with that vessel. During the primary
season, each vessel authorized to fish in that season under paragraph
(a) of this section may take, retain, possess, and land sablefish, up
to the cumulative limits for each of the permits registered for use
with that vessel (i.e., stacked permits). If multiple limited entry
permits with sablefish endorsements are registered for use with a
single vessel, that vessel may land up to the total of all cumulative
limits announced in this paragraph for the tiers for those permits,
except as limited by paragraph (b)(3)(ii) of this section. Up to 3
permits may be registered for use with a single vessel during the
primary season; thus, a single vessel may not take and retain, possess
or land more than 3 primary season sablefish cumulative limits in any
one year. A vessel registered for use with multiple
[[Page 62532]]
limited entry permits is subject to per vessel limits for species other
than sablefish, and to per vessel limits when participating in the
daily trip limit fishery for sablefish under Sec. 660.232. In 2021,
the following annual limits are in effect: Tier 1 at 58,649 lb (26,602
kg), Tier 2 at 26,659 lb (12,092 kg), and Tier 3 at 15,234 lb (6,910
kg). In 2022 and beyond, the following annual limits are in effect:
Tier 1 at 55,858 lb (25,337 kg), Tier 2 at 25,390 lb (11,517 kg), and
Tier 3 at 14,509 lb (6,581 kg).
* * * * *
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10. Revise Tables 2 (North) and 2 (South) to subpart E to read as
follows:
[GRAPHIC] [TIFF OMITTED] TP02OC20.038
[[Page 62533]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.039
0
11. Revise Tables 3 (North) and 3 (South) to subpart F to read as
follows:
[[Page 62534]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.040
[[Page 62535]]
[GRAPHIC] [TIFF OMITTED] TP02OC20.041
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12. Amend Sec. 660.360 by revising paragraphs (c)(1) introductory
text, (c)(1)(i)(B), (C), and (D), (c)(2)(i)(B) and (D), (c)(3)(i)(A),
and (c)(3)(ii)(B) to read as follows:
Sec. 660.360 Recreational fishery--management measures.
* * * * *
(c) * * *
(1) Washington. For each person engaged in recreational fishing off
the coast of Washington, the groundfish bag limit is 9 groundfish per
day, including rockfish, cabezon and lingcod. Within the groundfish bag
limit, there are sub-limits for rockfish, lingcod, and cabezon
[[Page 62536]]
outlined in paragraph (c)(1)(i)(D) of this section. In addition to the
groundfish bag limit of 9, there will be a flatfish limit of 5 fish,
not to be counted towards the groundfish bag limit but in addition to
it. The recreational groundfish fishery will open the second Saturday
in March through the third Saturday in October for all species. In the
Pacific halibut fisheries, retention of groundfish is governed in part
by annual management measures for Pacific halibut fisheries, which are
published in the Federal Register. The following seasons, closed areas,
sub-limits and size limits apply:
(i) * * *
(B) South coast recreational yelloweye rockfish conservation area.
Recreational fishing for groundfish and halibut is allowed within the
South Coast Recreational YRCA. The South Coast Recreational YRCA is
defined by latitude and longitude coordinates specified at Sec.
660.70.
(C) Westport offshore recreational yelloweye rockfish conservation
area. Recreational fishing for groundfish and halibut is allowed within
the Westport Offshore Recreational YRCA. The Westport Offshore
Recreational YRCA is defined by latitude and longitude coordinates
specified at Sec. 660.70.
(D) Recreational rockfish conservation area. Fishing for groundfish
with recreational gear is prohibited within the recreational RCA unless
otherwise stated. It is unlawful to take and retain, possess, or land
groundfish taken with recreational gear within the recreational RCA
unless otherwise stated. A vessel fishing in the recreational RCA may
not be in possession of any groundfish unless otherwise stated. [For
example, if a vessel participates in the recreational salmon fishery
within the RCA, the vessel cannot be in possession of groundfish while
in the RCA. The vessel may, however, on the same trip fish for and
retain groundfish shoreward of the RCA on the return trip to port.]
Coordinates approximating boundary lines at the 10- fm (18 m) through
40-fm (73-m) depth contours can be found at Sec. 660.71. The
Washington recreational fishing season structure is as follows:
[GRAPHIC] [TIFF OMITTED] TP02OC20.042
* * * * *
(2) * * *
(i) * * *
(B) Recreational rockfish conservation area (RCA). Fishing for
groundfish with recreational gear is prohibited within the recreational
RCA, a type of closed area or groundfish conservation area, except with
long-leader gear (as defined at Sec. 660.351). It is unlawful to take
and retain, possess, or land groundfish taken with recreational gear
within the recreational RCA, except with long-leader gear (as defined
at Sec. 660.351). A vessel fishing in the recreational RCA may not be
in possession of any groundfish. [For example, if a vessel fishes in
the recreational salmon fishery within the RCA, the vessel cannot be in
possession of groundfish while within the RCA. The vessel may, however,
on the same trip fish for and retain groundfish shoreward of the RCA on
the return trip to port.] Off Oregon, from January 1 through December
31, recreational fishing for groundfish is allowed in all depths.
Coordinates approximating boundary lines at the 10-fm (18 m) through
40-fm (73-m) depth contours can be found at Sec. 660.71.
* * * * *
(D) In the Pacific halibut fisheries. Retention of groundfish is
governed in part by annual management measures for Pacific halibut
fisheries, which are published in the Federal Register. Between the
Columbia River and Humbug Mountain, during days open to the ``all-
depth'' sport halibut fisheries, when Pacific halibut are onboard the
vessel, no groundfish, except sablefish, Pacific cod, and other species
of flatfish
[[Page 62537]]
(sole, flounder, sanddab), may be taken and retained, possessed or
landed, except with long-leader gear (as defined at Sec. 660.351).
``All-depth'' season days are established in the annual management
measures for Pacific halibut fisheries, which are published in the
Federal Register and are announced on the NMFS Pacific halibut hotline,
1-800-662-9825.
* * * * *
(3) * * *
(i) * * *
(A) Recreational rockfish conservation areas. The recreational RCAs
are areas that are closed to recreational fishing for groundfish.
Fishing for groundfish with recreational gear is prohibited within the
recreational RCA, except that recreational fishing for species in the
Other Flatfish complex, petrale sole, and starry flounder is permitted
within the recreational RCA as specified in paragraph (c)(3)(iv) of
this section. It is unlawful to take and retain, possess, or land
groundfish taken with recreational gear within the recreational RCA,
unless otherwise authorized in this section. A vessel fishing in the
recreational RCA may not be in possession of any species prohibited by
the restrictions that apply within the recreational RCA. For example,
if a vessel fishes in the recreational salmon fishery within the RCA,
the vessel cannot be in possession of rockfish while in the RCA. The
vessel may, however, on the same trip fish for and retain rockfish
shoreward of the RCA on the return trip to port. If the season is
closed for a species or species group, fishing for that species or
species group is prohibited both within the recreational RCA and
shoreward of the recreational RCA, unless otherwise authorized in this
section. Coordinates approximating boundary lines at the 10- fm (18 m)
through 40-fm (73-m) depth contours can be found at Sec. 660.71. The
California recreational fishing season structure and RCA depth
boundaries by management area and month are as follows:
[GRAPHIC] [TIFF OMITTED] TP02OC20.043
* * * * *
(ii) * * *
(B) Bag limits, hook limits. In times and areas when the
recreational season for the RCG Complex is open, there is a limit of 2
hooks and 1 line when fishing for the RCG complex and lingcod. The bag
limit is 10 RCG Complex fish per day coastwide, with a sub-bag limit of
5 fish for vermilion rockfish. This sub-bag limit counts towards the
bag limit for the RCG Complex and is not in addition to that limit.
Retention of yelloweye rockfish, bronzespotted rockfish, and cowcod is
prohibited. Multi-day limits are authorized by a valid permit issued by
California and must not exceed the daily limit multiplied by the number
of days in the fishing trip.
* * * * *
[FR Doc. 2020-21783 Filed 10-1-20; 8:45 am]
BILLING CODE 3510-22-P