Magnuson-Stevens Act Provisions; Fisheries Off West Coast States; Pacific Coast Groundfish Fishery; 2019-20 Biennial Specifications and Management Measures, 47416-47483 [2018-19460]
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Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 660
[Docket No. 180625576–8576–01]
RIN 0648–BH93
Magnuson-Stevens Act Provisions;
Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery;
2019–20 Biennial Specifications and
Management Measures
SUPPLEMENTARY INFORMATION:
Electronic Access
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 2019–20 harvest
specifications and management
measures 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. This proposed rule
would also revise the management
measures that are intended to keep the
total catch of each groundfish stock or
stock complex within the harvest
specifications. The 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.
DATES: Comments must be received no
later than October 19, 2018.
ADDRESSES: Submit your comments,
identified by NOAA–NMFS–2018–0056,
by either of the following methods:
• Federal e-Rulemaking Portal: Go to
www.regulations.gov/
#!docketDetail;D=NOAA-NMFS-20180056, click the ‘‘Comment Now!’’ icon,
complete the required fields, and enter
or attach your comments.
• 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
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SUMMARY:
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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 2018 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.
Executive Summary
Purpose of the Regulatory Action
This proposed rule would implement
the 2019–20 harvest specifications and
management measures for groundfish
stock taken in the U.S. exclusive
economic zone off the coasts of
Washington, Oregon, and California.
The purpose of this proposed rule is to
conserve and manage Pacific Coast
groundfish fishery resources to prevent
overfishing, to rebuild overfished
stocks, achieve optimum yield (OY),
and ensure that management measures
are based on the best scientific
information available. This action
proposes harvest specifications for
2019–20 consistent with existing or
revised default harvest control rules for
all stocks, and establishes management
measures designed to keep catch within
the appropriate limits. The harvest
specifications are set consistent with the
OY harvest management framework
described in Chapter 4 of the Pacific
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Coast Groundfish Fishery Management
Plan (PCGFMP).
Major Provisions
This proposed rule contains two types
of major provisions. The first are the
harvest specifications (overfishing limits
(OFLs), acceptable biological catches
(ABCs), and annual catch limits (ACLs)),
and the second are management
measures designed to keep fishing
mortality within the ACLs. The Council
developed the harvest specifications
(OFLs, ABCs, and ACLs) in this rule
through a rigorous scientific review and
decision making process, which is
described later in this proposed rule.
The OFL is the maximum sustainable
yield (MSY) harvest level and is an
estimate of the catch level above which
overfishing is occurring. The Pacific
Fishery Management Council’s
(Council) Scientific and Statistical
Committee (SSC) recommends OFLs
based on the best scientific information
available. The ABC is an annual catch
specification that is the stock or stock
complex’s OFL reduced by an estimate
of scientific uncertainty. The SSCrecommended method for incorporating
scientific uncertainty is referred to as
the P star-sigma approach, which 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 ACL is a harvest
specification set equal to or below the
ABC. The Council recommends ACLs at
a level that should achieve OY from the
fishery, which is the amount of fish that
will provide the greatest overall benefit
to the Nation, particularly with respect
to food production and recreational
opportunities, and taking into account
the protection of marine ecosystems.
The ACLs are based on consideration of
conservation objectives, socio-economic
concerns, management uncertainty, and
other factors. All known sources of
fishing and scientific research catch are
counted against the ACL. Many stocks
are further allocated into harvest
guidelines (HGs) or annual catch targets
(ACTs) for the purposes of dividing
catch between different gear types and
sectors or building in a precautionary
approach to prevent catch from
exceeding an ACL.
This proposed rule includes harvest
specifications for the two overfished
stocks managed under the PCGFMP,
yelloweye rockfish and cowcod. For the
2019–20 biennium, NMFS proposes
changes to the yelloweye rockfish
rebuilding plan, due to its improved
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stock rebuilding outlook and changes to
the needs of fishing communities,
described under section C of this rule.
This proposed rule would modify the
harvest control rule for this stock and
establish harvest specifications and
management measures consistent with
those revisions. The other overfished
stock, cowcod, continues to have a
positive rebuilding outlook, and no
changes to its rebuilding plan are
proposed. Therefore, this rule proposes
to establish harvest specifications
consistent with the existing rebuilding
plan provisions for this stock. Since the
2017–18 biennium, three stocks have
been declared rebuilt: Darkblotched
rockfish, bocaccio rockfish (bocaccio),
and Pacific ocean perch. The harvest
control rules for these stocks revert back
to those established prior to the stock
being declared overfished.
To keep mortality of the stocks
managed under the PCGFMP within the
ACLs, the Council also recommended
management measures. Generally
speaking, management measures are
intended to rebuild overfished stocks,
prevent catch from exceeding the ACLs,
and allow for the harvest of healthy
stocks. Management measures include
time and area restrictions, gear
restrictions, trip or bag limits, size
limits, and other management tools.
Management measures may vary by
fishing sector because different fishing
sectors require different types of
management to control catch. Most of
the management measures the Council
recommended for 2019–20 were slight
variations to existing management
measures, and do not represent a change
from current management practices.
Additionally, the Council recommended
several new management measures,
including: Establishment of salmon
bycatch mitigation measures,
modifications to depth restrictions in
the Western Cowcod Conservation Area
(CCA), modification of discard mortality
rates for IFQ lingcod and sablefish,
removal of the Shorebased Individual
Fishing Quota (IFQ) Program daily
vessel limits, removal of the automatic
authority on at-sea set-asides,
continuation of the IFQ adaptive
management pass through, and
modification of the retention ratios for
incidentally caught lingcod in the
salmon troll fishery.
Table of Contents
I. Background
A. Specification and Management Measure
Development Process
II. Harvest Specifications
A. Proposed OFLs for 2019 and 2020
B. Proposed ABCs for 2019 and 2020
C. Proposed ACLs for 2019 and 2020
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D. Summary of ACL Changes From 2018 to
2019–20
III. Management Measures
A. Deductions From the ACLs
B. Stock Complex Composition
Restructuring
C. Biennial Fishery Allocations
D. Tribal Fisheries
E. Routine Modifications to the Boundaries
Defining Rockfish Conservation Areas
(RCAs)
F. Limited Entry Trawl
G. Limited Entry Fixed Gear and Open
Access Nontrawl Fishery
H. Recreational Fisheries
I. Salmon Bycatch Mitigation Measures
J. Modifications to Depth Restrictions
Within the Western CCA
K. Modification of Lingcod and Sablefish
Discard Mortality Rates
L. Removal of IFQ Daily Vessel Limits
M. Removal of Automatic Authority for
Darkblotched Rockfish and Pacific Ocean
Perch Set-Asides for At-Sea Sector
N. Continuation of Adaptive Management
Pass Through
O. Modification of the Incidental Lingcod
Retention Ratio in the Salmon Troll
Fishery
P. Administrative Actions
IV. Classification
I. Background
The PCGFMP requires the harvest
specifications and management
measures for groundfish to be set at least
biennially. This proposed rule is based
on the Council’s final recommendations
made at its June 2018 meeting, as well
as harvest specifications for some stocks
adopted at the Council’s April 2018
meeting.
A. Specification and Management
Measure Development Process
The Northwest Fisheries Science
Center (NWFSC) conducted full stock
assessments in 2017 for 9 of the 128
stocks 1 included under the PCGFMP
(Blue/deacon rockfish (CA, WA, OR),
California scorpionfish, lingcod [north
and south], Pacific ocean perch,
yellowtail rockfish north of 40°10′ N
lat., yelloweye rockfish). Additionally,
the NWFSC conducted assessment
updates that run new data through
existing models for eight stocks
(arrowtooth flounder, blackgill rockfish
south of 40°10′ N lat., bocaccio S of 43°
N lat., darkblotched rockfish). The
NWFSC did not update assessments for
the remaining stocks, so harvest
specifications for these stocks are based
on assessments from previous years.
The stock assessment reports are
available on the Council website
(https://www.pcouncil.org/).
The Council’s stock assessment
review panel (STAR panel) reviews the
1 Stocks for which ACLs or ACL contributions to
stock complex ACLs are calculated.
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stock assessments, including data
moderate assessments, for technical
merit, and to determine that each stock
assessment document is sufficiently
complete. Finally, the SSC reviews the
stock assessment and STAR panel
reports and makes recommendations to
the Council.
When spawning stock biomass (B)
falls below the minimum stock size
threshold (MSST), a stock is declared
overfished, and the Council must
develop a rebuilding plan that sets the
strategy for rebuilding the stock to BMSY
in the shortest time possible, while
considering needs of fishing
communities and other factors. The
current MSST reference point for
assessed flatfish stocks is 12.5 percent of
initial biomass or B12.5%. For all other
assessed groundfish stocks, the current
MSST reference point is 25 percent of
initial biomass or B25%. The following
overfished groundfish stocks would
continue be managed under rebuilding
plans in 2019–20: Cowcod south of
40°10′ N lat. and yelloweye rockfish.
For overfished stocks, in addition to
any stock assessments or stock
assessment updates, the NWFSC may
also prepare rebuilding analyses. The
rebuilding analysis is used to project the
future status of the overfished resource
under a variety of alternative harvest
strategies and to determine the
probability of recovering to BMSY or its
proxy within a specified timeframe.
The Council considered new stock
assessments, stock assessment updates,
a rebuilding analysis for yelloweye
rockfish, public comment, and advice
from its advisory bodies over the course
of six Council meetings during
development of its recommendations for
the 2019–20 harvest specifications and
management measures. At each Council
meeting between June 2017 and June
2018, the Council made a series of
decisions and recommendations that
were, in some cases, refined after further
analysis and discussion. Detailed
information, including the supporting
documentation the Council considered
at each meeting is available at the
Council’s website, www.pcouncil.org.
The 2019–20 biennial management
cycle was the second cycle following
PCGFMP Amendment 24 (80 FR 12567,
March 10, 2015), which established
default harvest control rules and
included an Environmental Impact
Statement (EIS). The EIS described the
ongoing implementation of the PCGFMP
and default harvest control rules, along
with ten-year projections for harvest
specifications and a range of
management measures. Under
Amendment 24, the default harvest
control rules used to determine the
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previous biennium’s harvest
specifications (i.e., OFLs, ABCs, and
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 unless the
Council makes a different
recommendation. Therefore, this rule
implements the default harvest control
rules, consistent with Amendment 24,
for most stocks, and discusses
departures from the defaults. The
Analysis identifies the preferred
alternative harvest control rules, new
management measures, and other
decision points that were not described
in the 2015 EIS and is posted on the
NMFS WCR web page (see
SUPPLEMENTARY INFORMATION) along with
this proposed rule.
Information regarding the OFLs,
ABCs, and ACLs proposed for
groundfish stocks and stock complexes
in 2019–20 is presented below, followed
by a discussion of the proposed
management measures for commercial
and recreational groundfish fisheries.
II. Harvest Specifications
This proposed rule would set 2019–20
harvest specifications and management
measures for all of the 128 groundfish
stocks which 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.
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 categories to define OFLs and
ABCs based on the level of reliable
information available to fishery
scientists. 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-atlength, 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
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number of stocks for which some
biological indicators are available, yet
status is based on a ‘‘data-moderate’’
quantitative 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 (DBSRA), depletion corrected
average catch (DCAC), and average
catches) are used to determine the OFL
for category three stocks.
A. Proposed OFLs for 2019 and 2020
The SSC derives OFLs for groundfish
stocks with stock assessments by
applying the harvest rate to the current
estimated biomass. Fx% harvest rates
represent the rates of fishing mortality
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).
For 2019–20, the Council maintained
its policy of using a default harvest rate
as a proxy for the fishing mortality rate
that is expected to achieve the
maximum sustainable yield (FMSY). A
proxy is used because there is
insufficient information for most Pacific
Coast groundfish stocks to estimate
stock-specific FMSY values. Taxonspecific proxy fishing mortality rates are
used due to perceived differences in the
productivity among different taxa of
groundfish. A lower value is used for
stocks with relatively high resilience to
fishing while higher values are used for
less resilient stocks with low
productivity. In 2019–20, the Council
proposed the following default harvest
rate proxies, 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), F40% for Pacific
whiting, 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.
Stocks may be grouped into
complexes for various reasons,
including: When stocks in a
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multispecies fishery cannot be targeted
independently of one another and MSY
cannot be defined on a stock-by-stock
basis; when there is insufficient data to
measure the stocks’ status; or when it is
not feasible for fishermen to distinguish
individual stocks among their catch.
Most groundfish stocks managed in a
stock complex are data-poor stocks
without full stock assessments. The
proposed OFLs for stock complexes are
the sum of the OFL contributions for the
component stocks, when known. In the
2017–18 harvest specifications, there
were eight stock complexes used to
manage groundfish stocks pursuant to
the PCGFMP. These stock complexes
were: (1) Minor Nearshore Rockfish
north; (2) Minor Nearshore Rockfish
south; (3) Minor Shelf Rockfish north;
(4) Minor Shelf Rockfish south (5)
Minor Slope Rockfish north; (6) Minor
Slope Rockfish south; (7) Other Flatfish;
and (8) Other Fish. This rule proposes
the following changes to stock
complexes: (1) Remove blue/deacon
rockfish from the Minor Nearshore
Rockfish north complex and group with
Oregon black rockfish to create a new
complex (Oregon black rockfish/blue
rockfish/deacon rockfish); (2) remove
Washington kelp greenling from the
Other Fish complex and pair with
Washington cabezon to create a new
complex (Washington cabezon/kelp
greenling); (3) remove Oregon kelp
greenling from the Other Fish complex
and pair with Oregon cabezon to create
a new complex (Oregon cabezon/kelp
greenling). This proposed rule, if
approved, would increase the total of
number of stock complexes from eight
to eleven.
A detailed description of the scientific
basis for all of the SSC-recommended
OFLs proposed in this rule is included
in the Stock Assessment and Fishery
Evaluation (SAFE) document for 2018,
available at the Council’s website,
www.pcouncil.org.
B. Proposed ABCs for 2019 and 2020
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 establish
the ABC. 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. 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
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uncertainty beyond the sigma value
reduction. The PCGFMP specifies that
the upper limit of P* will be 0.45. In
combination, the P* and s values
determine the amount by which the
OFL will be reduced to establish the
SSC-endorsed ABC.
The SSC quantified major sources of
scientific uncertainty in the estimates of
OFLs and generally recommended a s
value of 0.36 for category one stocks, a
s value of 0.72 for category two stocks,
and a s value of 1.44 for category three
stocks. For category two and three
stocks, there is greater scientific
uncertainty in the OFL estimate because
the assessments for these stock
assessments 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
quantitative stock assessments.
Assuming the same P* is applied, a
larger s value results in a larger
reduction from the OFL. For 2019–20,
the Council continued the general
policy of using the SSC-recommended s
values for each stock category. However,
the SSC made a few exceptions to the
standard s values assigned to each
category. For some stocks, the SSC did
not deem the proxy s values the best
scientific information available because
the uncertainty in estimated spawning
biomass is greater than the s used as a
proxy for other stocks in that category.
For 2019–20, the SSC calculated unique
s values for five stocks. For kelp
greenling off Oregon, a category 1 stock,
the SSC calculated a s value of 0.44,
which is more precautionary than the
standard s value of 0.36 for this
category of stocks. For aurora rockfish,
also a category 1 stock, the SSC
calculated a s value of 0.39. And for
California scorpionfish, the SSC
calculated a s value of 0.582. The SSC
also calculated a s value of 0.783 for
California blue/deacon rockfish, and a s
value of 0.803 for Oregon blue/deacon
rockfish, both category 2 stocks. These
s values are higher than the standard s
value of 0.72 for this category of stocks.
For 2019–20, the Council maintained
the P* policies it established for the
previous biennium for most stocks. As
was done in 2015–16 and 2017–18, the
Council recommended using P* values
of 0.45 for all individually managed
category one stock, except sablefish.
Combining the category one s value of
0.36 with the P* value of 0.45 results in
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a reduction of 4.4 percent from the OFL
when deriving the ABC. For category
two and three stocks, the Council’s
general policy was to use a P* of 0.4,
with a few exceptions. The Council
recommended a P* of 0.45 for all of the
stocks managed in the Minor Rockfish
complexes and the Other Fish complex,
as was done in 2017–18. When
combined with the s values of 0.72 and
1.44 for category two and three stocks,
a P* value of 0.40 corresponds to 16.7
percent and 30.6 percent reductions,
respectively. The Council recommended
using P* values of 0.40 for all
individually managed category two and
three stocks, except those described
below. The Council recommended a P*
of 0.45 for big skate, black rockfish off
Oregon, cowcod, English sole, and
yellowtail rockfish south of 40°10′ N
lat., as was done in 2015–16 and 2017–
18, because there was no new scientific
information indicating a change in P*
value was warranted.
C. Proposed ACLs for 2019 and 2020
The Council recommends ACLs for
each stock and stock complex that is ‘‘in
the fishery’’, as defined in the PCGFMP.
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 the
precautionary threshold, 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.
Alternatively, even if a stock biomass is
larger than BMSY, an ACL may be set
below the ABC to address conservation
objectives, socioeconomic concerns,
management uncertainty, or other
factors necessary to meet management
objectives.
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,
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47419
January 6, 2015; 80 FR 12567, March 10,
2015).
Many groundfish stocks are managed
with stock-specific harvest
specifications. Often these stocks are
category one or category two stocks and
their stock status is known. The default
harvest control rule for stocks with
biomass estimates above MSY is to set
the ACL equal to the ABC. The default
harvest control rule for stocks with
biomass estimates below MSY but above
the overfished threshold is to set the
ACL below the ABC using a standard
reduction on the harvest rate, which is
described in the proposed and final
rules for the 2015–16 biennium (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. Both ACL harvest
control rules are applied after the ABC
deduction is made. 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.
These harvest policies foster a quicker
return to the BMSY level and serve as an
interim rebuilding policy for stocks that
are below the MSST.
All of the ACLs for stock complexes
are less than or equal to the summed
ABC contributions of each component
stock in each complex. Default harvest
control rules are based on stock status.
Thus, when the Council revises the
stock composition of a stock complex,
the default harvest control rule may
adjust based on status of the stocks that
remain in the complex.
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. For many of the
stocks or stock complexes in the fishery,
the Council chose to maintain the
default harvest control rules from the
previous biennial cycle. Table 1
presents a summary table of the
proposed changes to ACL policies for
certain stocks for 2019–20.
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TABLE 1—PROPOSED CHANGES TO HARVEST CONTROL RULES FOR 2019–20
Alternative
Harvest control rule
CA Scorpionfish S
of 34°27′ N lat.
Lingcod N of 40°10′
N lat.
Current ...........................
Proposed change ...........
Current ...........................
150 mt constant catch ACL ................................................................................
ACL = ABC (P* = 0.45) .......................................................................................
ACL = ABC (P* = 0.45 in OR & WA; P* = 0.4 in CA) w/40–10 adj. for the CA
contribution to the ABC and ACL Assumes 1,000 mt and 750 mt removals
for 2017 and 2018 in the north and south, respectively and full ACL attainment thereafter.
ACL = ABC (P* = 0.45) w/40–10 adj. for the CA contribution to the ABC and
ACL Assumes 40% and 75% ACL attainment for 2017 and 2018 in the
north and south, respectively and full ACL attainment thereafter.
ACL = ABC (P* = 0.4) w/40–10 adj. Assumes 1,000 mt and 750 mt removals
for 2017 and 2018 in the north and south, respectively and full ACL attainment thereafter.
ACL = ABC (P* = 0.45) w/40–10 adj. Assumes 40% and 75% ACL attainment
for 2017 and 2018 in the north and south, respectively and full ACL attainment thereafter.
ABC (P* = 0.4), ACL (SPR = 76.0%); TTARGET = 2027 .....................................
ABC (P* = 0.4), ACL (SPR = 65.0%); TTARGET = 2029 .....................................
Proposed change ...........
Lingcod S of 40°10′
N lat.
Current ...........................
Proposed change ...........
Yelloweye Rockfish
a Current
Current ...........................
Proposed change ...........
150 mt
313 mt
3,110 mt
4,871 mt
1,144 mt
1,039 mt
20 mt
48 mt
ACL is for 2018, Proposed change ACL is for 2019.
The following sections discuss
proposed ACLs for the stocks for which
the Council’s recommended ACLs
depart from the existing default harvest
control rule.
California Scorpionfish
For the 2017–18 biennium, the default
harvest control rule set the ACL for
California scorpionfish at a constant
value of 150 mt rather than on a ratebased value. The NWFSC conducted a
new assessment of California
scorpionfish south of 34°27′ N lat. in
2017. The assessment indicated the
stock was healthy at a 54 percent
depletion at the start of 2017. The
Council recommended and NMFS is
proposing an alternative harvest control
rule for California scorpionfish. The
revised harvest control rule would set
the ACL equal to the ABC using a P*
value of 0.45, consistent with other
category one stocks. The resulting 2019–
20 ACLs would more than double
compared to the 2018 ACL under this
new harvest control rule. The stock is
projected to remain healthy (i.e., greater
than 40 percent depletion) for the next
ten years under the proposed alternative
harvest control rule.
Lingcod
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ACL a
Stock
The NWFSC conducted two
assessments for lingcod in 2017—one
each for the areas north and south of the
California/Oregon border at 42° N lat.
Current spawning stock biomass is
estimated to be 57.9 percent in the
northern assessment area relative to
unfished spawning biomass, and has
continued to increase over the last five
years as a result of high recruitment in
2008 and 2013. Current spawning stock
biomass is estimated to be 32.1 percent
in the southern assessment area relative
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to unfished spawning biomass.
Although spawning biomass in the
southern assessment area is estimated to
have been increasing in recent years,
recruitment is estimated to have been
well below average over the last 10 to
15 years, which suggests that stock
biomass is not increasing for the
southern portion of the stock at the
same rate as for the northern portion of
the stock. The SSC endorsed the 2017
north and south lingcod stock
assessments as the best scientific
information available for status
determination and management, and
designated both portions of the stock as
category one. The stocks had been
previously managed as category two
stocks. The current harvest control rule
sets the ACL equal to the ABC for the
portion of the northern stock off Oregon,
but applies the 40–10 precautionary
reduction to the portion of the northern
stock off California (i.e., between 42°
and 40°10′ N lat.), and to the whole of
the southern stock using the most recent
5-year (2012–2016) average percentage
of swept area biomass estimates.
This proposed rule would change the
P* value from 0.4 to 0.45 for both
portions of the stock, reflecting greater
confidence in the current stock
assessments. The resulting 2019 and
2020 ACLs for the northern portion of
the stock would increase by
approximately 64 percent and 68
percent, respectively, compared to the
2018 ACL under this new harvest
control rule. The resulting 2019 and
2020 ACL under this new harvest
control rule for the southern portion of
the stock would decrease by
approximately 9 percent and 24 percent,
respectively, compared to the 2018 ACL.
This proposed action is expected to
allow moderate growth of the stock
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under an average recruitment
assumption in the next ten years.
Overfished Stocks and Changes to
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
discusses several previously overfished
stocks that have rebuilt since the last
biennium, as well as provisions for the
two remaining overfished stocks in the
PCGFMP, namely cowcod south of
40°10′ N lat. and yelloweye rockfish.
The Council proposed cowcod ACLs for
2019 and 2020 based on the current
cowcod 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 history of each overfished
stock, and can be found at https://
www.pcouncil.org/groundfish/
fisherymanagement-plan/.
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Stocks Rebuilt Since Last Biennium
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 2019–20 biennium,
three stocks were declared rebuilt:
Bocaccio, Pacific ocean perch, and
darkblotched rockfish. In addition to the
harvest control rules for these stocks
reverting back to the defaults for the
2019–20 biennium, other requirements
for overfished stocks are removed. One
such change is that these stocks would
no longer be listed under the priority
stock observer reporting requirements at
§ 660.140(h)(1)(i)(3). This proposed
change is described further under the
heading, P. Administrative Actions, in
this preamble.
Yelloweye Rockfish (Sebastes
Ruberrimus)
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. The current rebuilding plan
parameters include an SPR harvest rate
of 76 percent and a median target time
for rebuilding (TTARGET) of 2074 (the
year for which there is a 50 percent
probability that the stock is rebuilt). The
NWFSC conducted a new stock
assessment for yelloweye rockfish in
2017, and the SSC conducted a
rebuilding analysis using the updated
assessment. The rebuilding analysis
includes a recalculation of rebuilding
parameters that inform the Council’s
decision-making process. According to
the rebuilding analysis, should the
Council decide to revise the existing
rebuilding plan, the new minimum time
to rebuild (TMIN; the time to rebuild if
there was no fishing) would be 2026 and
TTARGET would be changed from 2074
(in the 2011 assessment) to 2027 (in the
2017 assessment). Under the current
harvest control rule, the ACL for
yelloweye would increase to 29 mt and
30 mt in 2019 and 2020, respectively, an
increase from 20 mt in 2018. This
improvement in stock status outlook is
due to several factors, including: Lower
than expected catches of yelloweye
rockfish in recent years; a more
optimistic value on stock recruit
steepness, which corresponds to a more
productive stock; and strong year
classes entering the spawning
population in recent years.
As a result of the improvement in
stock outlook, the Council
recommended, and NMFS is proposing,
changing the SPR harvest rate for
yelloweye rockfish to 65 percent and
changing the TTARGET to 2029. This
change in the rebuilding plan would
47421
allow an ACL for yelloweye rockfish of
48 mt in 2019 and 49 mt in 2020.
Within the ACL, for 2019, the Council
recommended a fishery harvest
guideline (HG) of 42.1 mt, of which 3.4
mt is the trawl HG and 38.6 mt is the
nontrawl HG. For 2020, NMFS proposes
a fishery HG of 42.1 mt, of which 3.4 is
the trawl HG and 39.5 is the nontrawl
HG. For more discussion of the use of
HGs, see section II (Harvest
Specifications), C, entitled ‘‘C. Biennial
Fishery Allocations’’ in this preamble.
Additionally, the Council
recommended, and NMFS is proposing,
to establish Annual Catch Targets
(ACTs) within the nontrawl allocation
HG. The nontrawl sector includes the
limited entry fixed gear and open access
fixed gear 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. Table 2 outlines the
harvest specifications that were in place
for yelloweye rockfish for 2018 for
comparison purposes. Tables 3 and 4
outline the proposed harvest
specifications for 2019 and 2020 for
yelloweye rockfish.
TABLE 2—2018 HARVEST SPECIFICATIONS FOR YELLOWEYE ROCKFISH
All sectors ........................................................................................................
Nontrawl ....................................................................................................
Non-Nearshore ..................................................................................
Nearshore ..........................................................................................
Washington Recreational ..................................................................
Oregon Recreational .........................................................................
California Recreational ......................................................................
Trawl .........................................................................................................
OFL
(mt)
ABC
(mt)
ACL
(mt)
HG
(mt)
58
........................
........................
........................
........................
........................
........................
........................
48
........................
........................
........................
........................
........................
........................
........................
20
........................
........................
........................
........................
........................
........................
........................
14
12.9
0.7
2.0
3.3
3
3.9
1.1
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TABLE 3—2019 HARVEST SPECIFICATIONS FOR YELLOWEYE ROCKFISH
All sectors ............................................................................
Nontrawl ........................................................................
Non-Nearshore ......................................................
Nearshore ..............................................................
Washington Recreational ......................................
Oregon Recreational .............................................
California Recreational ..........................................
Trawl .............................................................................
OFL
(mt)
ABC
(mt)
ACL
(mt)
HG
(mt)
82
........................
........................
........................
........................
........................
........................
........................
74
........................
........................
........................
........................
........................
........................
........................
48
........................
........................
........................
........................
........................
........................
........................
ACT
(mt)
42
38.6
2.0
6.0
10.0
8.9
11.6
3.4
........................
........................
1.6
4.7
7.8
7.0
9.1
........................
TABLE 4—2020 HARVEST SPECIFICATIONS FOR YELLOWEYE ROCKFISH
OFL
(mt)
All sectors ............................................................................
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84
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(mt)
77
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(mt)
49
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(mt)
43
........................
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TABLE 4—2020 HARVEST SPECIFICATIONS FOR YELLOWEYE ROCKFISH—Continued
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Nontrawl ........................................................................
Non-Nearshore ......................................................
Nearshore ..............................................................
Washington Recreational ......................................
Oregon Recreational .............................................
California Recreational ..........................................
Trawl .............................................................................
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 how encounter
rates will change under the proposed
higher catch limits and the associated
suite of management measures that
should allow for an overall expansion of
groundfish fishery effort (see section
4.2.1.3 of the Analysis). 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 overfished
stock by this sector.
The Analysis demonstrates how the
proposed changes to the rebuilding plan
select a TTARGET that is as short as
possible, while giving consideration to
the status and biology of the overfished
species and the needs of the fishing
communities, consistent with Section
303(e)(4) of the Magnuson-Stevens Act
(see Appendix B of the Analysis). The
Council indicated that a new default
harvest control rule may more
appropriately account for the needs of
West Coast communities by providing
greater opportunity in both commercial
and recreational groundfish sectors and
improving income stability for
dependent communities.
West Coast fishing communities
depend on a portfolio of commercial
and recreational fisheries to support
year-round operations. Recent
coastwide declines in commercial
fisheries for Dungeness crab, salmon,
sardines, tuna, pink shrimp, halibut,
and other non-groundfish stocks due to
changing environmental conditions and
changes in management have created
considerable instability for many
communities. Additionally, many of
these communities have experienced
substantial declines in recreational
fishing activity, notably for salmon and
for tuna (see Section B.1.1. of Appendix
B). Groundfish fishing activity has
traditionally helped communities
weather cyclical changes in abundance
in other non-groundfish fisheries.
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OFL
(mt)
ABC
(mt)
ACL
(mt)
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
However, the restrictions in catch of
target groundfish stocks necessary to
support rebuilding of overfished
groundfish stocks over the past 15 years
has limited both commercial and
recreational groundfish fishing
opportunities. The loss of groundfish
fishing opportunities further affects
fishing communities through loss of
processor activity and loss of business
for support services.
The proposed change to the yelloweye
rockfish rebuilding plan is intended to
support continued yelloweye rebuilding
progress while providing more stability
for coastal communities through
increased access to co-occurring target
stocks. Yelloweye rockfish bycatch is
rare and unpredictable, but can occur in
sporadic ‘‘lightning strikes’’ of large
magnitude. Because yelloweye rockfish
catch is difficult to predict, the Council
has constrained yelloweye rockfish
catch below the ACL set in the current
rebuilding plan by conservatively
managing co-occurring target stocks.
This proposed rebuilding plan would
increase the estimated TTARGET by two
years, from 2027 to 2029, which is still
within the required 10-year rebuilding
timeframe specified in section 304(e)(4)
of the Magnuson-Stevens Act, but which
would more than double the yelloweye
rockfish ACL in 2019 compared to 2018.
The higher ACLs resulting from the
revised rebuilding plan allow a suite of
management measures that could
expand groundfish fishing
opportunities. For commercial trawl
vessels, this proposed action would
facilitate more trading of yelloweye
rockfish allocation, which should allow
for less risk-averse fishing strategies and
as a result, an increase in attainment of
underutilized stocks, including lingcod,
chilipepper rockfish, and Pacific cod
(see Section B.5.2.3 of Appendix B of
the Analysis). For commercial fixed gear
vessels, the yelloweye rockfish ACL
increases could support future actions
to consider reopening the nontrawl
Rockfish Conservation Area or to
consider increasing trip limits for target
stocks such as lingcod (see Section
B.5.2.2 of Appendix B of the Analysis).
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HG
(mt)
ACT
(mt)
39.5
2.1
6.2
10.2
9.1
11.9
3.4
........................
1.7
4.9
8.1
7.2
9.4
........................
In addition, the proposed increases in
the yelloweye rockfish ACL would
allow for additional research
opportunities to collect much-needed
data to better inform stock assessments
and management decisions (see Section
B.1.3 of Appendix B of the Analysis).
Recreational fishing opportunities
would have the greatest potential for
expansion from this proposed action.
For the recreational sectors in
communities off Washington, Oregon,
and California, the proposed change to
the rebuilding plan and higher ACLs
would allow shorter periods of time
with depth restrictions in place and
access to deeper depths during seasons
with depth restrictions. Allowing
recreational fishermen to access
additional fishing grounds should allow
them to target a broader suite of stocks,
such as yellowtail rockfish, lingcod, and
chilipepper rockfish, while also
reducing pressure on sensitive
nearshore stocks such as black rockfish
(see Section B.5.3 of Appendix B of the
Analysis). This increase in recreational
effort would especially benefit the
communities of Neah Bay, WA;
Winchester Bay, OR; and Fort Bragg,
CA, which are highly dependent on
recreational opportunities (see Section
B.5 of Appendix B of the Analysis).
D. Summary of ACL Changes From 2018
to 2019–20
Table 5 compares the ACLs for major
stocks for 2018, 2019, and 2020. Due to
proposed changes in stock complex
composition, not all stocks are shown
below. Many stocks would have higher
ACLs in 2019 and 2020 than in 2018.
The only stock that would have an ACL
more than 10 percent below the 2018
ACL is starry flounder. The change in
stock abundance for starry flounder is
largely driven by a change in the way
the stock is assessed, which better
accounts for the uncertainty in the stock
status of this data poor stock. As a
result, for 2019–20, starry flounder has
a more precautionary OFL, ABC, and
ACL. Overall attainment of starry
flounder has been low in recent years,
so this change is not expected to have
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a substantial impact on the fleet (see
47423
Section A.3.4 of Appendix A of the
Analysis).
TABLE 5—ACLS FOR MAJOR STOCKS FOR 2018, 2019, AND 2020
[Overfished stocks are capitalized]
Area
COWCOD .........................................
YELLOWEYE ROCKFISH ................
Arrowtooth Flounder .........................
Big Skate ...........................................
Black Rockfish ..................................
Black Rockfish ..................................
Bocaccio a .........................................
Cabezon ............................................
California Scorpionfish ......................
Canary Rockfish ................................
Chilipepper Rockfish .........................
Darkblotched Rockfish a ....................
Dover Sole ........................................
English Sole ......................................
Lingcod ..............................................
Lingcod ..............................................
Longnose skate .................................
Longspine Thornyhead .....................
Longspine Thornyhead .....................
Pacific Cod ........................................
Pacific Ocean Perch a .......................
Petrale Sole ......................................
Sablefish ...........................................
Sablefish ...........................................
Shortbelly Rockfish ...........................
Shortspine Thornyhead .....................
Shortspine Thornyhead .....................
Spiny Dogfish ....................................
Splitnose Rockfish ............................
Starry Flounder .................................
Widow Rockfish ................................
Yellowtail Rockfish ............................
S of 40°10′ N lat ...............................
Coastwide .........................................
Coastwide .........................................
Coastwide .........................................
California (S of 42° N lat.) ................
Washington (N of 46°16′ N lat.) .......
S of 40°10′ N lat ...............................
California (S of 42° N lat.) ................
S of 34°27′ N lat ...............................
Coastwide .........................................
S of 40°10′ N lat ...............................
Coastwide .........................................
Coastwide .........................................
Coastwide .........................................
N of 40°10′ N lat ..............................
S of 40°10′ N lat ...............................
Coastwide .........................................
N of 34°27′ N lat ..............................
S of 34°27′ N lat ...............................
Coastwide .........................................
N of 40°10′ N lat ..............................
Coastwide .........................................
N of 36° N lat ...................................
S of 36° N lat ...................................
Coastwide .........................................
N of 34°27′ N lat ..............................
S of 34°27′ N lat ...............................
Coastwide .........................................
S of 40°10′ N lat ...............................
Coastwide .........................................
Coastwide .........................................
N of 40°10′ N lat ..............................
a Stock
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2018 ACL
(mt)
Stock
10
20
13,743
494
332
301
741
149
150
1,526
2,507
653
50,000
7,537
3,110
1,144
2,000
2,747
867
1,600
281
3,013
5,475
1,944
500
1,698
898
2,083
1,761
1,282
12,655
6,002
2019 ACL
(mt)
10
48
15,574
494
329
298
2,097
147
313
1,450
2,536
765
50,000
10,090
4,871
1,039
2,000
2,603
822
1,600
4,340
2,908
5,606
1,990
500
1,683
890
2,071
1,750
452
11,831
5,997
2020 ACL
(mt)
10
49
12,750
494
326
297
2,011
146
307
1,368
2,410
815
50,000
10,135
4,541
869
2,000
2,470
780
1,600
4,229
2,845
5,723
2,032
500
1,669
883
2,059
1,731
452
11,199
5,716
Percent
change 2018
to 2019
0
140
13
0
¥1
¥1
183
¥1
108
¥5
1
17
0
34
57
¥9
0
¥5
¥5
0
1444
¥3
2
2
0
¥1
¥1
¥1
¥1
¥65
¥7
0
was declared rebuilt in 2017.
III. Management Measures
A. Deductions From the ACLs
This section describes biennial fishery
harvest guidelines and set-asides used
to further allocate the ACLs to the
various components on the fishery,
routine management measures to
control fishing, and new management
measures proposed for 2019–20.
Routine management measures for the
commercial fishery modify fishing
behavior during the fishing year to
ensure that catch is constrained below
the ACL, and include trip and
cumulative landing limits, time/area
closures, size limits, and gear
restrictions. Routine management
measures for the recreational fisheries
include bag limits, size limits, gear
restrictions, fish dressing requirements,
and time/area closures. New
management measures proposed for the
2019–20 biennial cycle would work in
combination with current management
measures to control fishing effort/
activity.
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 set aside fish for certain types
of activities. Off the top deductions
account for four distinct sources of
groundfish mortality: 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 exempted fishing permits
(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.
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B. Stock Complex Composition
Restructuring
The Council recommended, and
NMFS is proposing, modifications to the
existing stock complexes used for
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harvest specifications and management
that would create three new stock
complexes. Changes in the composition
of stock complexes do not affect the
underlying harvest specifications
because the stock complex ACL is
simply the sum of the constituent
stocks’ specifications. The stocks in the
proposed stock complex restructuring
are predominately shallow water
nearshore stocks that occur primarily
within state waters. Nearly all the
removals for these stocks are attributed
to the recreational and commercial
nearshore fisheries that are subject to
joint state and Federal management.
The first modification would remove
Oregon blue/deacon rockfish (BDR)
from the Nearshore Rockfish complex
north of 40°10′ N latitude and pair it
with Oregon black rockfish to form a
new Oregon black/BDR complex. The
second modification would remove
Oregon and Washington kelp greenling
and Washington cabezon from the Other
Fish complex to form two new stock
complexes: An Oregon Kelp Greenling/
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Cabezon Complex and a Washington
Kelp Greenling/Cabezon Complex. The
objectives of the stock complex
proposals are: (1) Better alignment of
stocks per the complex goals and
definitions as defined in the PCGFMP
and National Standard 1 of the
Magnuson-Stevens Act; (2) reduced
management complexity; and 3)
enhanced management flexibility (e.g.,
greater ability to take inseason actions).
These proposed changes to stock
complex composition better comply
with the National Standard 1 guidelines,
which recommend stocks managed in a
stock complex ‘‘should have a similar
geographic distribution, life history
characteristics, and vulnerabilities to
fishing pressure such that the impact of
management actions on the stocks is
similar.’’ These complex proposals
pertain primarily to the commercial
nearshore and recreational fisheries, as
these are shallow water stocks
infrequently encountered by the trawl
sectors or other fisheries.
Oregon Black/Blue/Deacon Rockfish
Complex
The Council recommended removing
Oregon BDR rockfish from the
Nearshore Rockfish complex north of
40°10′ N. latitude, and pairing it with
Oregon black rockfish, which is
currently managed individually, to form
a new Oregon black/BDR complex. Note
that blue and deacon rockfish are
separate stocks, but they are referred to
collectively since they were assessed
together and therefore have joint harvest
specifications. Blue/deacon rockfish are
more frequently found in the middle of
the water column, whereas the other
stocks in the Nearshore Rockfish
complex are more strongly associated
with benthic habitats. Oregon black
rockfish is an important target fishery,
especially in the recreational sector. As
detailed in Section C.3 of Appendix C
of the Analysis, this proposed action
would better align management of
Oregon BDR rockfish with black
rockfish, a stock that is also a midwater
stock and often co-occurs with BDR
rockfish. The proposed action would
provide more targeted management of
Oregon BDR rockfish by moving Oregon
BDR from a larger stock complex to a
much smaller one. However, this action
could have the potential to provide less
targeted management for black rockfish
by moving it from individual
management into a complex. The risk of
less targeted management would be that
catch could exceed the stock’s ACL
contribution while remaining under the
overall complex ACL.
As a measure to prevent negative
effects on black rockfish as a result of
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moving it into a complex, the Council
recommended and NMFS is proposing
an HG for the stock at its ACL
contribution level to the complex. For
2019, the HG would be 515.8 mt, and for
2020, 512.2 mt. Additionally, as
discussed in Section 4.3.1.3 of the
Analysis, Oregon Department of Fish
and Wildlife (ODFW) intends to
implement mitigation measures to
prevent any change in the risk of
overfishing for Oregon black rockfish.
These measures include establishing
and managing catch against state harvest
guidelines for the component stocks of
the new BDR complex, shortening the
state catch reporting time lag from one
month to one week to allow for rapid
state-level management response, and
revising ODFW inseason catch
projection methods to better monitor
rapid periodic increases in recreational
fishing effort. ODFW has also proposed
action within its state regulations to
reduce its aggregate state recreational
bag limit from seven to five fish per day,
which could slow the overall catch rate
during the recreational season. Finally,
NMFS’s recent approval of longleader
fishing gear for use in waters off Oregon
(83 FR 13428; March 29, 2018) could
shift some fishing effort away from
black rockfish and towards
underutilized midwater stocks,
primarily widow and yellowtail
rockfish. If this change to the stock
complex structure is approved, these
additional measures would ensure a
level of management scrutiny for black
rockfish similar to the level it would
receive if it were managed individually.
Other Fish Complex
The Other Fish complex originated as
a compilation of stocks that did not
match well with other complexes.
Because the complex is composed of
biologically dissimilar stocks (e.g.,
ratfish, skates, sharks, grenadier,
greenling, cabezon, and codling), the
grouping has not supported practical
management of its component stocks.
Over time, the Council has redesignated
some stocks in the original complex as
ecosystem components, or has removed
some stocks from the complex for
individual management (e.g., big skate,
82 FR 9634; February 7, 2017). This
proposed action would remove three
stocks from the Other Fish complex and
incorporate them into two new
complexes to allow for more accurate
management of these stocks. This action
would also require the addition of
scientific sorting requirements for the
limited entry trawl, limited entry fixed
gear, and open access fixed gear. These
sorting requirements would allow
proper accounting of the catch of
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component stock in these new
complexes separate from the Other Fish
complex.
Oregon Kelp Greenling/Cabezon
Complex
This proposed action would remove
Oregon kelp greenling from the Other
Fish complex and pair it with Oregon
cabezon, which is currently managed
individually, to create the Oregon Kelp
Greenling/Cabezon Complex. This
proposed action was recommended
because these stocks share a greater
similarity to each other (e.g., both are
solitary nearshore stocks that often cooccur) compared to the other stocks
within the Other Fish complex. As a
measure to prevent any increase in the
risk of overfishing for cabezon as a
result of moving it into a complex, the
Council recommended and NMFS is
proposing a HG for the stock at its ACL
contribution level to the complex. For
2019 and 2020, the HG would be 46.8
mt. The mitigation measures ODFW
intends to implement for the Oregon
black/BRD complex, described above,
would similarly help prevent adverse
effects on cabezon from moving from
individual management into a stock
complex.
Washington Kelp Greenling/Cabezon
Complex
This proposed action would remove
Washington kelp greenling and
Washington cabezon from the Other
Fish complex to form a Washington
Kelp Greenling/Cabezon Complex. In
Washington, kelp greenling and cabezon
are retained in recreational groundfish
fisheries. They are nearshore stocks that
are generally not targeted and often cooccur. As both of the stocks are
currently managed within a larger
complex, moving them to their own
complex would provide more targeted
management. As part of this proposed
action, the Washington Department of
Fish and Wildlife would be better able
to implement inseason management
actions for these stocks, if needed.
C. Biennial Fishery Allocations
The Council recommends two-year
trawl and nontrawl allocations during
the biennial specifications process for
all stocks without long-term allocations
or stocks where the long-term allocation
is suspended because the stock is
declared overfished. For all stocks,
except sablefish north of 36° N lat., the
Council recommends allocations for the
trawl and nontrawl sectors 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
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(Management Measures), A, entitled
‘‘Deductions from the ACLs,’’ in this
preamble. The two-year allocations and
recreational harvest guidelines are
designed to accommodate anticipated
mortality in each sector as well as
variability and uncertainty in those
mortality estimates. 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.
Big Skate
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shown in Table 6 for big skate in 2019
and 2020. These allocations are
anticipated to accommodate estimates of
mortality of big skate, by sector, in
2019–20.
The Council recommended and
NMFS is proposing the allocations
TABLE 6—2019 AND 2020 TRAWL/NONTRAWL ALLOCATIONS OF BIG SKATE
Percentage
Nontrawl ...................................................................................................................................................................
Trawl ........................................................................................................................................................................
Bocaccio
recommended and NMFS is proposing
the allocations shown in Table 7 for
bocaccio in 2019 and 2020. These
allocations are anticipated to
Bocaccio was declared rebuilt since
last biennium. The Council
5
95
Allocation
(mt)
22.6
429.5
accommodate estimates of mortality of
bocaccio, by sector, in 2019–20 and
address the stock’s newly rebuilt status.
TABLE 7—2019 AND 2020 ALLOCATIONS OF BOCACCIO
2019 HG
(mt)
Trawl ........................................................................................................................................................................
Non-nearshore .........................................................................................................................................................
Nearshore ................................................................................................................................................................
California recreational ..............................................................................................................................................
Canary Rockfish
Table 8 for canary rockfish in 2019 and
2020. These allocations are anticipated
to accommodate estimates of mortality
The Council recommended and
NMFS is proposing the allocations in
2020 HG
(mt)
800.7
382.0
4.8
863.4
767.1
366.0
4.6
827.2
of canary rockfish, by sector, in 2019–
20, and maintain the same allocation
scheme as in 2018.
TABLE 8—2019 AND 2020 ALLOCATIONS OF CANARY ROCKFISH
2019 HG
(mt)
Shorebased IFQ Program .......................................................................................................................................
At-sea Sectors .........................................................................................................................................................
Catcher/processor ............................................................................................................................................
Mothership ........................................................................................................................................................
Non-nearshore .........................................................................................................................................................
Nearshore ................................................................................................................................................................
Washington recreational ..........................................................................................................................................
Oregon recreational .................................................................................................................................................
California recreational ..............................................................................................................................................
Cowcod
For 2019–20, the Council
recommended and NMFS is proposing
setting a cowcod ACT at 6 mt, and
having it function as a fishery harvest
guideline similar to the ACT in the
2017–18 biennium; it is the amount that
would be allocated across groundfish
fisheries. Table 9 shows the trawl/
nontrawl allocations for cowcod for
2020 HG
(mt)
953.6
46
16
30
43.8
94.3
47.1
70.7
127.3
894.3
46
16
30
41.2
88.7
44.3
66.5
119.7
2019 and 2020. NMFS anticipates the
proposed allocation structure will keep
catch below the 2019–20 cowcod ACT,
and NMFS maintains the same
allocation scheme as in 2018.
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TABLE 9—2019 AND 2020 TRAWL/NONTRAWL ALLOCATIONS OF COWCOD
Percentage
Nontrawl ...................................................................................................................................................................
Trawl ........................................................................................................................................................................
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36
64
Allocation
(mt)
2.2
3.8
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Longnose Skate
The Council recommended and
NMFS is proposing the trawl/nontrawl
allocations for longnose skate in Table
10. The allocation percentages reflect
historical catch of longnose skate in the
two sectors, and NMFS maintains the
same allocation scheme that was in
place for longnose skate in 2018.
TABLE 10—2019 AND 2020 TRAWL/NONTRAWL ALLOCATIONS OF LONGNOSE SKATE
Percentage
Nontrawl ...................................................................................................................................................................
Trawl ........................................................................................................................................................................
Minor Nearshore Rockfish
Harvest specifications for Minor
Nearshore Rockfish north of 40°10′ N
lat. are proposed to decrease from the
103.2 mt in 2017–18 to 81 mt in 2019
and 92 mt in 2020 due to the proposed
removal of Oregon black rockfish from
the complex.
The states intend to manage catch
using state-specific harvest guidelines:
18.6 mt for Washington; 23.2 mt for
Oregon, and 36.6 mt for California for
2019. For 2020, 18.3 mt for Washington;
23.0 mt for Oregon, and 37.9 mt for
California. However, instead of
implementing state specific harvest
guidelines in Federal regulations, the
state Council representatives from
Oregon and Washington committed to
heightened inseason communication
regarding catches of stocks managed in
the complex, relative to the harvest
guidelines, consistent with the current
state coordinated management. Under
state management, landed component
stocks within the Minor Nearshore
Rockfish complex must be sorted by
stock. Because the states may also take
inseason action independent of NMFS,
10
90
Allocation
(mt)
185.2
1,666.5
the proposed action is not anticipated to
result in exceeding the complex ACL in
2019–20.
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 2019
and 2020 are shown in Table 12. This
maintains the same allocation
percentages as have been in place for
the Minor Shelf Rockfish complexes
since 2011.
TABLE 12—TRAWL/NONTRAWL ALLOCATIONS FOR MINOR SHELF ROCKFISH NORTH AND SOUTH OF 40°10′ N LAT.
Percentage
Minor Shelf Rockfish north of 40°10′ N lat .............................
Minor Shelf Rockfish south of 40°10′ N lat .............................
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Minor Slope Rockfish
Minor Slope Rockfish were allocated
between the trawl and nontrawl
fisheries in PCGFMP Amendment 21.
This action applies those Amendment
21 allocation percentages to the updated
2019–20 fishery harvest guidelines.
Blackgill rockfish in California was
assessed in 2011 and has continued to
be managed within the Minor Slope
Rockfish complex, but with a stockspecific HG south of 40°10′ N lat.
beginning in 2013. For 2019–20 the
Council recommended a blackgill
rockfish harvest guideline equal to the
ABC contribution for the portion of the
stock south of 40°10′ N lat.; this harvest
guideline is 159 mt for 2019 and 2020.
D. Tribal Fisheries
Tribes implement management
measures for Tribal fisheries both
independently as sovereign
governments and cooperatively with the
management measures in the Federal
regulations. The Tribes may adjust their
Tribal fishery management measures
inseason to stay within the Tribal
harvest targets and estimated impacts to
overfished stocks. The only change to
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Trawl ......................................
Nontrawl .................................
Trawl ......................................
Nontrawl .................................
Tribal harvest targets and management
measures proposed for the 2019–20
biennium is an increase in the petrale
sole harvest target from 220 mt to 290
mt.
The Tribes proposed trip limit
management in Tribal fisheries for
2019–20 for several stocks, including
several rockfish stocks and stock
complexes. This rule proposes
maintaining the same trip limits for
Tribal fisheries as those in place in
2018. For rockfish stocks, Tribal
regulations will continue to require full
retention of all overfished rockfish
stocks and marketable non-overfished
rockfish stocks. The 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.
E. Routine Modifications to the
Boundaries Defining Rockfish
Conservation Areas
Rockfish Conservation Areas (RCAs)
are large area closures intended to
reduce the catch of a stock or stock
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60.2
39.8
12.2
87.8
2019 HG
1,190
786.9
188.6
1,357.3
2020 HG
1,186.6
784.5
188.6
1,357.3
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 2019–20 biennium, the
Council recommended minor
adjustments to the 75 fathom (fm) (137
m), 100 fm (183 m), 125 fm (229 m), and
150 fm (274 m) depth contours off of
California to more accurately refine the
depth contours. These proposed
modifications would adjust boundaries
for RCAs around Santa Cruz Island,
Spanish Canyon, Delgada Canyon,
Cordell Bank, Point Ano Nuevo, San
Miguel Island, and Anacapa Island.
Additionally, this proposed rule
would correct the coordinates for the
125 fm (229 m) depth contour
recommended by the Council in June
2017 around Usal Canyon and Noyo
Canyon. The Council recommended
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these modifications to fix errors that
were discovered during a previous
change to the RCA line from 150 fm
(274 m) to 125 fm (229 m) as part of the
2017–18 harvest specifications and
management measures (82 FR 9634;
February 7, 2017). When NMFS
implemented changes to the RCA line,
it was determined that the latitude and
longitude coordinates for several areas
were crossed over between 125 and 150
fathoms. These proposed changes would
provide access to canyons that were
previously open when the 150 fm (274
m) line was in effect, and which were
intended to be open after the previous
changes to the RCA line.
complex. For all stocks except big skate,
this rule proposes maintaining the same
IFQ fishery trip limits for these stocks
for the start of the 2019–20 biennium as
those in place in 2018. For big skate, the
Council proposes reverting trip limits to
those implemented at the start of the
2017–18 biennium. 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 are
considered a routine measure under
§ 660.60(c), and may be implemented or
adjusted, if determined necessary,
through inseason action.
F. Limited Entry Trawl
G. Limited Entry Fixed Gear and Open
Access Nontrawl Fishery
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°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
Management measures for the limited
entry fixed gear (LEFG) and open access
(OA) nontrawl fisheries tend to be
similar because the majority of
participants in both fisheries use hookand-line gear. Management measures,
including area restrictions 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 2019–20
47427
biennium, changes to management
measures include: changes to trip limits
for sablefish, minor slope rockfish and
darkblotched rockfish, canary rockfish,
lingcod, shortspine rockfish, and
longspine rockfish. Proposed 2019–20
trip limits for these changes 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 raising the trip limits for the
LEFG fleet from those in 2018 between
75 to 100 lb (34 to 45 kg) a week
depending on the period of the year. For
the OA fleet, the trip limits would be
the same as in 2018. For the portion
south of 36° N lat., the Council
recommended the limited entry and
open access trip limits remain the same
as those in 2018. The proposed sablefish
trip limits for 2019–20 are shown in
Table 13.
TABLE 13—SABLEFISH TRIP LIMITS FOR LIMITED ENTRY AND OPEN ACCESS SECTORS NORTH AND SOUTH OF 36° N LAT.
Sector
Area
Limited entry .....................
north of 36° N lat ............
1,200 lb/week; not to exceed 3,600 lb bi-monthly.
south of 36° N lat ...........
2,000 lb/week.
north of 36° N lat ............
300 lb daily, or one landing per week up to 1,000 lb, not to exceed 2,000 lb bi-monthly.
south of 36° N lat ...........
300 lb daily, or 1 landing per week up to 1,600 lb, not to exceed 3,200 lb bimonthly.
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Open Access ....................
Minor Slope Rockfish and Darkblotched
Rockfish Trip Limits
In the 2017–18 biennium, the trip
limit for minor slope rockfish and
darkblotched rockfish for the OA sector
was linked to the landed weight of
sablefish for the trip. The current trip
limit for minor slope rockfish and
darkblotched rockfish north of 40°10′ N
lat. is no more than 25 percent of the
landed weight of sablefish per trip,
which corresponds to a maximum of
500 lb (227 kg) bi-monthly (25 percent
of the 2,000 lb (907 kg) bi-monthly limit
of sablefish). This is an aggregate limit
for all stocks combined. For 2019–20,
the Council proposed and NMFS is
recommending decoupling this limit
from the landed weight of sablefish and
instead creating a stand-alone trip limit
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Jan–Feb
Mar–Apr
May–Jun
for minor slope rockfish and
darkblotched rockfish of 500 lb (227 kg)
per month (all stocks combined). The
new limit would be double the current
limit. The Council recommended and
NMFS is proposing the new trip limit
structure because it would be simpler
for OA participants to abide by and
would better allow them to retain more,
and discard less, of their incidental
catches.
Canary Rockfish Trip Limits
The Council recommended and
NMFS is proposing that canary rockfish
retention would be permitted in the
LEFG sector between 40°10′ N latitude
and 34°27′ N latitude, with a trip limit
of 300 pounds per two months. For the
area south of 34°27′ N latitude, the trip
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Jul–Aug
Sept–Oct
Nov–Dec
limit would be the same, except for a
closure during Period 2 (March-April).
For OA, the structure would be similar,
with a 150 lb (68 kg) per two months
limit, and a closure during Period 2
(March-April) south of 40°10′ N
latitude. These proposed closures for
the canary rockfish trip limits would
align with the trip limit structure for the
Minor Shelf Rockfish, Deeper Nearshore
Rockfish, Shallow Nearshore Rockfish,
California scorpionfish, and lingcod
south of 40°10′ N lat. Establishing a
canary rockfish bi-monthly trip limit
that matches the Shelf Rockfish trip
limit would provide a uniform approach
for monitoring, management, and law
enforcement. Table 14 shows the
proposed trip limits for 2019 and 2020
for canary rockfish.
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TABLE 14—PROPOSED CANARY ROCKFISH TRIP LIMITS FOR LIMITED ENTRY AND OPEN ACCESS SECTORS
Sector
Area
Jan–Feb
Limited entry .....................
N of 40°10′ N lat ............
300 lb/2 months.
40°10′ N lat.—34°27′ N
lat.
300 lb/2 months.
S of 34°27′ N lat .............
Open Access ....................
300 lb/2
months.
Mar–Apr
May–Jun
CLOSED ....
N of 40°10′ N lat ............
S of 40°10′ N lat .............
Lingcod Trip Limits
Lingcod is managed north and south
of 40°10´ N lat. The Council
recommends OFLs, ABCs, ACLs, and
HGs separately for each of these stocks.
Historically, the Council has also
recommended trip limits for LEFG and
OA for each of these two stocks. For
2019–20, the Council proposed and
NMFS is recommending two separate
LEFG and OA trip limits for lingcod
north of 40°10´ N lat.: one set of trip
limits for the area north of 42° N lat.,
and one set of trip limits for the area
Jul–Aug
Sept–Oct
Nov–Dec
300 lb/2 months.
150 lb/2 months.
50 lb/2
months.
CLOSED ....
150 lb/2 months.
between 42° N lat. and 40°10´ N lat. The
new latitude break would allow more
flexibility for alternative management
strategies by state agencies to promote
fishing opportunity while staying
within state-specific yelloweye rockfish
shares. In addition, this new latitude
break aligns with the 42° N lat.
latitudinal break used in the stock
assessment (see Section A.2.6 of
Appendix A of the Analysis). This
proposed rule would establish a trip
limit for LEFG of 2,000 lb (907 kg) per
2 months for the area north of 42° N lat.
and a trip limit of 1,400 lb (635 kg) per
2 months for the area between 42° N lat.
and 40°10´ N lat. For OA, this rule
would establish a trip limit of 900 lb
(408 kg) per 2 months for the area north
of 42° N lat., and a trip limit of 600 lb
(272 kg) per 2 months for the area
between 42° N lat. and 40°10´ N lat.
Overall, the lingcod trip limits proposed
for 2019–20 are higher than those in
place in 2018, which is possible due to
higher ACLs for co-occurring yelloweye
rockfish. Table 15 below shows
proposed trip limits for lingcod north of
40°10´ N lat.
TABLE 15—PROPOSED LINGCOD TRIP LIMITS NORTH OF 40°10′ N LAT.
Sector
Area
Limited entry .....................
North of 42° N lat ...........
2,000 lb/2 months.
42° N Lat. to 40°10´ N lat
1,400 lb/2 months.
N of 42° N lat .................
900 lb/month.
42° N Lat. to 40°10´ N lat
600 lb/month.
Open access ....................
For lingcod south of 40°10´ N lat.,
ACLs for the 2019–20 biennium are
Jan–Feb
Mar–Apr
May–Jun
lower compared to 2018. Therefore, this
rule proposes reductions to lingcod trip
Jul–Aug
Sept–Oct
Nov–Dec
limits for both LEFG and OA. Table 16
below shows proposed trip limits.
TABLE 16—PROPOSED LINGCOD TRIP LIMITS SOUTH OF 40°10´ N LAT.
Sector
Area
Jan–Feb
Limited entry .....................
200 lb/2 months .............
CLOSED ....
Open Access ....................
300 lb/month ..................
CLOSED ....
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Shortspine and Longspine Rockfish Trip
Limits
Retention of shortspine and longspine
thornyheads is currently prohibited
year-round for the OA sector north of
34°27´ N lat. This proposed rule would
provide a 50 lb (23 kg) per month trip
limit for shortspine and longspine
thornyheads north of 40°10´ N lat. only.
Retention would continue to be
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800 lb/2
months.
May–Jun
1,200 lb/2 months
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Sept–Oct
600 lb/ ........
month .........
Nov–Dec
300 lb/
month.
300 lb/month.
prohibited for OA from 40°10´ N lat. to
34°27´ N lat. The Council recommended
and NMFS is proposing this trip limit
based on an industry recommendation
to allow retention of incidental catches.
The current retention prohibition is
likely a holdover from when there were
separate LEFG and OA allocations of
thornyheads under the nontrawl
allocation. OA attainment of longspine
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and shortspine thornyheads north of
34°27´ N latitude would be expected to
remain low under this proposed rule, as
they continue to be an incidental catch
rather than a targeted stock.
Primary Sablefish Tier Limits
Some limited entry fixed gear permits
are endorsed to receive annual sablefish
quota, or tier limits. Vessels registered
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Oregon
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 align
the lingcod season in Marine Area 4
with the recreational groundfish season
and the lingcod season in Marine Areas
1–3. This adjustment would allow for an
additional month of fishing in Marine
Area 4 compared to 2018. Additionally,
the proposed rule would allow retention
of yellowtail and widow rockfish
seaward of 20 fm (37 m) in July and
August in Marine Areas 3 and 4. The
aggregate groundfish bag limits off
Washington would continue to be nine
fish in all areas. However, the sub-bag
limit for canary rockfish, previously 2
fish in all marine areas, would be
removed, and the cabezon sub-bag limit
would be changed from two fish per day
to one fish for all marine areas.
Additionally, this rule proposes
removing the 18-in (45.7-cm) minimum
size limit for cabezon in Marine Area 4.
The Council recommended these
changes, which allow more access to
target stocks with fewer restrictions,
supported by the proposed increases to
the yelloweye rockfish ACL described in
Section C of this rule.
Consistent with the 2017–18
biennium, the Council proposed
continuing 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, the South Coast Recreational
YRCA, and the Westport Offshore
YRCA. Coordinates for YRCAs are
defined at § 660.70.
The Council recommended that size,
bag, and sub-bag limits would remain
the same as for 2018 for all stocks
except for lingcod. To keep within
allowable limits, the lingcod bag limit
would be split into separate limits for
north (42° N lat. (California/Oregon
border) to 40°10′ N lat. (Northern
Management Area)) and south (40°10′ N
lat. to the U.S. border with Mexico
(Mendocino Management Area, San
Francisco Management Area, Central
Management Area, and Southern
Management Area)). The Council
proposed maintaining the limit in the
north area at 2 lingcod per day, but
recommended reducing the limit in the
south area to 1 lingcod per day (down
from 2 in 2018). Additionally, this rule
proposes to allow year-round retention
of California scorpionfish in all
management areas, which is supported
by the proposed increase in the ACL for
this stock in 2019–20 described in
section II (Harvest Specifications), C,
entitled ‘‘Proposed ACLs for 2019 and
2020,’’ in this preamble.
H. Recreational Fisheries
This section describes the recreational
fisheries management measures
proposed for 2019–20. The Council
primarily recommends depth
restrictions and groundfish conservation
areas (GCAs) to constrain catch within
the recreational harvest guidelines for
each stock. Most of the changes to
recreational management measures are
modifications to existing measures.
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.
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The Council proposed that Oregon
recreational fisheries in 2019–20 would
operate under the same season
structures and GCAs as provided for
2017–18. This rule also proposes to
allow all-depth fishing in April, May,
and September. The Council’s proposed
expansions to fishing-depth access
during these months is supported by the
proposed increased yelloweye rockfish
ACL, described in section II (Harvest
Specifications) C, entitled, ‘‘Proposed
ACLs for 2019 and 2020,’’ of this
preamble. The Council proposed
maintaining the 2017–18 aggregate bag
limits and size limits in Oregon
recreational fisheries. 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).
California
The Council manages recreational
fisheries off of 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 17 shows the proposed season
structure and depth limits by
management area for 2019 and 2020.
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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 2019, Tier 1 at
47,637 lb (21,608 kg), Tier 2 at 21,653
lb (9,822 kg), and Tier 3 at 12,373 lb
(5,612 kg). In 2020 and beyond, the
following annual limits are in effect:
Tier 1 at 48,642 lb (22,064 kg), Tier 2
at 22,110 lb (10,029 kg), and Tier 3 at
12,634 lb (5,731 kg).
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I. Salmon Bycatch Mitigation Measures
In December 2017, NMFS completed
an Endangered Species Act (ESA)
consultation on the continued
implementation of the PCGFMP and
published a Biological Opinion
(available at https://www.pcouncil.org).
As part of its proposed action for the
consultation, the Council estimated
Chinook and coho catch in the whiting
and non-whiting groundfish fisheries.
The Council estimated that the whiting
sector (including tribal and non-tribal
vessels in the mothership, catcher/
processor (C/P), and Shoreside whiting
fleets) would take 11,000 Chinook
salmon and 474 coho salmon, and the
non-whiting sector (including tribal and
non-tribal vessels in the Shoreside
trawl, fixed gear, and recreational fleets)
would take 5,500 Chinook salmon and
560 coho salmon.
Additionally, the Council included in
its proposed action a reserve amount of
Chinook, 3,500 fish, in the event that
bycatch increases unexpectedly. The
reserve is a safeguard against catch
exceeding the total Chinook take
estimate, which is an immediate trigger
for reinitiation under section 7 of the
ESA. Either the whiting or non-whiting
sector, or both sectors, may access the
reserve in a given year, but the reserve
is limited to 3,500 Chinook total. Access
to the reserve is not guaranteed for
either sector. Accessing the reserve in
three out of any five consecutive years
will also trigger reinitiation of the ESA
consultation.
The incidental take statement (ITS)
includes six reasonable and prudent
measures (RPMs) that require the
Council and NMFS to take certain
actions to minimize take of endangered
and threatened Chinook and coho
salmon in Pacific Coast groundfish
fisheries. These RPMs are nondiscretionary, and were developed
based on the Biological Opinion’s
analysis of the Pacific Coast groundfish
fishery’s interactions with salmon. The
ITS provides terms and conditions
(T&C) under each RPM that are also
non-discretionary, and are required to
implement each specific RPM. Actions
performed in compliance with the terms
and conditions of the ITS are not
considered to be prohibited taking
under the ESA.
The Biological Opinion required that
specific T&Cs from the ITS must be
considered within the 2019–20 biennial
harvest specifications and management
measures process. These include: (1)
Review existing mechanisms in the
PCGFMP and regulations for avoiding
and reducing salmon bycatch to
determine if these measures are
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adequate to allow for timely inseason
management to keep the sectors from
exceeding their bycatch guidelines (T&C
2.a); (2) develop and implement initial
regulations governing the reserve of
3,500 Chinook salmon (T&C 3.a); and (3)
develop automatic closure mechanisms
if sectors exceed their bycatch guideline
and/or the reserve (T&C 3.c).
At its March 2018 meeting, the
Council’s Groundfish Management
Team (GMT) reviewed current
monitoring provisions in the PCGFMP,
existing mitigation measures, and
historical industry bycatch avoidance
tactics (see Section C.2 of Appendix C
of the Analysis). Additionally, the GMT
investigated salmon bycatch data by
area, depth, and time for the whiting
and non-whiting midwater trawl sectors
to determine if depth restrictions would
be effective for reducing salmon bycatch
(see Section C.3 of Appendix C of the
Analysis). As a result of that review, the
Council recommended modifications to
existing depth-based management tools
for salmon bycatch mitigation and the
creation of new depth-based
management tools to meet T&C 2.a. The
Council proposed: (1) Eliminating the
Ocean Salmon Conservation Zone
(OSCZ); (2) adding a new bycatch
reduction area (BRA) at the 200 fm (366
m) depth contour for vessels using
midwater trawl gear; (3) prohibiting the
use of midwater trawls and require the
use of selective flatfish trawls for any
bottom trawl vessels in the Columbia
River Salmon Conservation Zone
(CRSCZ) and the Klamath River Salmon
Conservation Zone (KRSCZ); and (4)
implementing automatic closure
mechanisms for the Chinook salmon
bycatch guidelines and reserve. The
Council and NMFS will continue to
implement other terms and conditions
in future rulemakings.
The proposed salmon bycatch
mitigation measures would protect ESAlisted salmon species, and help
maintain bycatch below the bycatch
guideline limits described in the
proposed action of the Biological
Opinion. Three of the four proposed
measures would benefit salmon by
managing bycatch in the groundfish
fisheries. The Council proposed
removing the OSCZ because the
Analysis suggested that this existing
provision is ineffective for reducing
salmon bycatch.
Ocean Salmon Conservation Zone
The OSCZ consists of all waters
shoreward of a boundary line
approximating the 100 fm (183 m) depth
contour. When NMFS projects that the
Pacific whiting fishery (tribal and nontribal) may take in excess of 11,000
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Chinook salmon within a calendar year,
NMFS implements a coastwide closure
in the OSCZ for all sectors (Pacific
whiting IFQ fishery, the catcher/
processor (C/P) sector, and the
mothership sector) through automatic
action. The OSCZ was first
implemented as an emergency rule,
effective from August 26, 2005, to
February 27, 2006 (70 FR 51682; August
31, 2005) as a means to reduce Chinook
salmon bycatch rates in nearshore areas.
NMFS later permanently added the
OSCZ as mechanism to limit Chinook
salmon interactions in the whiting
fishery during periods of high bycatch
(71 FR 78657; December 29, 2006).
NMFS has used this depth-based
management tool only once since
implementation. On October 20, 2014,
NMFS closed the OSCZ to Pacific
whiting vessels after determining the
Pacific whiting fishery took over 11,000
Chinook salmon.
The GMT concluded through its
review that the OSCZ provision is not
an effective tool for salmon bycatch
mitigation. Catch data from 2004 to
2017 demonstrates that, even in high
bycatch years, Chinook salmon catch in
the Pacific whiting fishery is not likely
to reach the 11,000 fish threshold until
the fall, around October. The C/P sector
and the mothership sector have not
fished in the depths within the OSCZ
after October since 2011, and the Pacific
whiting IFQ fishery has had minimal
activity within the depths of the OCSZ
after the fall (see section C.1.4 of
Appendix C of the Analysis). Therefore,
by the time the OSCZ would be
triggered by Chinook bycatch in the
groundfish fishery, none of the sectors
would be fishing in the area that would
be closed. For these reasons, NMFS
proposes to remove the OCSZ provision
from the regulations. Because this
provision has limited utility as a
bycatch management tool, NMFS does
not expect any discernable effects from
removing this provision from the
regulations.
Bycatch Reduction Areas (BRAs)
BRAs are depth-based management
provisions used to close waters
shallower than a specified depth
contour to fishing in order to minimize
impacts to groundfish or any prohibited
or protected species, such as salmon.
Under current regulations, NMFS, in
consultation with the Council and
through the routine management
process, can implement BRAs to close
areas shoreward of the 75-, 100-, and
150-fm (137-, 183-, and 274-m) depth
contours for a specific sector (i.e., C/P,
mothership, whiting IFQ, and Shoreside
IFQ Program non-whiting midwater).
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BRAs are also available through
automatic action if a whiting sector is
projected to reach or exceed a sectorspecific groundfish allocation prior to
attaining the whiting allocation.
However, the 75-, 100-, and 150-fm
(137-, 183-, and 274-m) BRAs are not
currently available for salmon bycatch
mitigation for any of the sectors and are
not proposed to be modified through
this action.
The Council recommended adding the
200-fm (366-m) depth contour as a BRA
available for implementation through
routine inseason action to mitigate
salmon bycatch in any of the groundfish
midwater trawl sectors. The groundfish
midwater trawl sectors subject to this
area closure would be the Pacific
whiting IFQ fishery, the C/P sector, and
the mothership sector, as well as the
non-whiting midwater trawl sector,
which primarily targets widow rockfish
and yellowtail rockfish. If the Council
and NMFS implemented the 200-fm
(366-m) BRA during a fishing season,
vessels using midwater trawl gear to
target either whiting or non-whiting
groundfish would be excluded from
waters shoreward of the 200-fm (366-m)
depth contour, but would still be
allowed to fish in waters seaward of
200-fm (366-m). This action would only
apply to non-tribal midwater trawl
vessels. NMFS expects that the Tribes
would implement area management
measures to mitigate salmon bycatch, if
necessary.
The Council and NMFS monitor the
salmon bycatch rates of the fleet
inseason. If any sector’s bycatch rates
exceed those considered in the
Biological Opinion, the Council and
NMFS could take inseason action to
implement the BRA for any of the
midwater trawl sectors. The effects of
this proposed action would depend on
these sectors’ ability to fish in areas
deeper than 200 fm (366 m). Section
C.1.4 of Appendix C of the Analysis
contains a description of the recent
catch data by depth. The shoreside
whiting trawl sector, and especially the
non-whiting midwater trawl sector,
would likely have limited or no ability
to fish seaward of 200 fm (366 m) due
to horsepower restrictions and because
the catch targets (canary rockfish,
widow rockfish, yellowtail rockfish) are
primarily found in shallower depths.
The sectors that would be unable to
effectively operate if the proposed BRA
were put into place would experience
negative economic effects from this
action. The level of economic impacts
would depend on when the BRA was
implemented. The non-whiting
midwater trawl fishery typically lands a
significant portion of its catch later in
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the year. Thus, if NMFS were to
implement a BRA after October, a
prohibition on fishing shoreward of 200
fm (366 m) could significantly reduce
this fleet’s landings of canary,
yellowtail, and widow rockfish. As
discussed in Section 4.3.1.1 of the
Analysis, on average, the non-whiting
midwater trawl fleet lands 25.8 percent
of its target stocks from October to
December.
The at-sea sectors have historically
been able to fish seaward of 200 fm (366
m), but in limited capacity. The MS
sector’s capacity to fish seaward of 200
fm (366 m) is particularly limited.
Additionally, data from the C/P and MS
sector from 2011 to 2017 has shown
higher amounts of incidental catch of
spiny dogfish, yellowtail rockfish, and
widow rockfish seaward of 200 fm (366
m), compared to shoreward of 200 fm
(Section C.1.4 of Appendix C of the
Analysis). Therefore, if NMFS
implements the 200-fm (366-m) BRA
and sectors choose to fish seaward of
200 fm (366 m) due to salmon bycatch
concerns, there could be increased
incidental catch of these stocks.
Incidental catch of widow rockfish by
the at-sea sector is managed under an
allocation, while catch of yellowtail
rockfish is managed under a set-aside
for the sector. Allocations are managed
more closely than set-asides. If an
allocation is exceeded, the fishery is
closed. Set-asides are generally managed
on an annual basis unless there is a risk
of overall catch exceeding an ACL for
the stock, unforeseen impacts on
another fishery, or conservation
concerns, in which case inseason action
may be taken. The at-sea sector’s catch
of both of these stocks has been at or
below allowable amounts in recent
years. For yellowtail rockfish, the
overall attainment of the ACL was
around 50 percent, so even if at-sea
catch increased, NMFS does not expect
the risk of exceeding the ACL to change.
Catch of spiny dogfish is managed
under an HG for the entire Pacific Coast
groundfish fishery, which ensures catch
will remain below the ACL for this
stock.
This proposed action, if approved,
would use the existing regulations for
inseason actions, which allow a single
meeting process. If the Council and
NMFS determine that any of the
midwater trawl sectors is encountering
Chinook salmon at a bycatch rate above
that analyzed in the Biological Opinion,
NMFS could issue a single Federal
Register notice to implement the BRA,
provided that waiver of notice and
comment meet the requirements of the
Administrative Procedure Act.
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Columbia River Salmon Conservation
Zone and the Klamath River Salmon
Conservation Zone
This proposed action would also close
the CRSCZ and the KRSCZ to all
midwater trawling and to bottom
trawling, unless vessels are using a
selective flatfish trawl (SFFT). This
action is a term and condition of the
Biological Opinion. Under current
regulations, vessels using midwater
trawl gear in the Pacific whiting primary
season are prohibited from fishing in the
CRSCZ and the KRSCZ. This proposed
action would extend the area
prohibition to vessels using midwater
trawl gear to target rockfish, including
widow rockfish and yellowtail rockfish,
a reemerging fishery following the
rebuilding of widow rockfish in 2012.
Additionally, this proposed action
would maintain protection for these
areas that is currently included under a
blanket requirement that groundfish
trawl vessels use SFFT gear shoreward
of the trawl RCA north of 40°10′ N lat.
Both the CRSCZ and KRSCZ are located
inside this area. NMFS proposed
removing this blanket requirement in a
separate proposed rule. This proposed
action would reestablish the SFFT
requirement inside the CRSCZ and
KRSCZ.
Bycatch Guideline and Reserve
Management
This proposed action would create a
provision in the regulations to give
NMFS automatic authority to close
either or both of the whiting and nonwhiting sector fisheries if: (1) Either
sector catches its guideline limit and the
reserve amount; or (2) either sector
reaches its guideline limit when the
other sector has already taken the
reserve amount. The closure would be
effective until the end of the fishing year
on December 31. This proposed measure
is a term and condition of the Biological
Opinion. However, the Council and
NMFS intend to use other available
tools, including area management tools,
to help manage salmon bycatch prior to
guideline limits being taken, with the
result of sectors being closed for the
remainder of the fishing year.
The proposed action organizes the
various sectors of the Pacific Coast
groundfish fishery into one of two
groupings: The whiting sector and the
non-whiting sector. The whiting sector
includes the tribal and non-tribal Pacific
whiting IFQ fishery, the C/P sector, and
the mothership sector. The non-whiting
sector includes the tribal and non-tribal
Shoreside IFQ Program, the LEFG
fishery, the OA fishery, and the
recreational fisheries off of Washington,
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Oregon, and California. The proposed
action includes only select recreational
fisheries that are not accounted for in
pre-season salmon modeling. The
recreational fisheries not accounted for
in preseason salmon modeling are those
occurring outside of the open salmon
seasons and the Oregon longleader
fishery. Any Chinook salmon bycatch in
these fisheries must be attributed to the
non-whiting threshold, and these
fisheries are subject to potential
closures. Chinook salmon bycatch from
each fishery accrues to the larger sector
(i.e., whiting or non-whiting) level. As
described in the Biological Opinion,
access to the reserve for additional
Chinook salmon bycatch above the
sector’s guideline limit is not
guaranteed. However, if one sector
surpasses its guideline limit, it may be
allowed to continue fishing, with
additional salmon bycatch accounted
for within the reserve. Under such a
scenario, if the sector’s bycatch reached
the reserve limit, all fisheries within
that sector would be subject to an
automatic closure. If one sector is
allowed to access the reserve in a given
calendar year, then the other sector,
upon reaching its guideline limit, would
be subject to an automatic closure rather
than potentially being able to access the
reserve.
Under the existing regulations for
automatic actions at § 660.60(d), a
closure notice would be published in
the Federal Register and be effective
immediately for all fisheries within
either or both of the whiting or nonwhiting sectors. NMFS waives notice
and comment under the Administrative
Procedure Act if good cause exists.
Section C.1.4 of Appendix C of the
Analysis describes the effects of this
proposed action on the whiting and
non-whiting sectors under different
scenarios, based on potential closures
lasting from either October or December
through the remainder of the fishing
year. Under any of the closure scenarios,
the effect on groundfish would be
reduced landings and underattainment
of the ACL for target stocks. The
economic effects of this action are
greatest under an October closure
scenario, and are least under a
December closure scenario.
The Analysis discusses that both the
bottom trawl and non-whiting midwater
trawl sectors typically have high catch
after October. Section 4.3.1.1 estimates
that an October closure would have the
greatest effect on the C/P fleet because,
on average, this fleet catches 45 percent
of its whiting catch between October
and the end of the year. Under the
December closure scenario, the average
percentage of target catch that could
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potentially be left unharvested ranges
from 0.5 percent for the Shoreside
whiting fleet to 13 percent for the
nonwhiting midwater trawl fleet.
Overall, Section C.4 of Appendix C of
the Analysis estimates that a closure
starting in October could have an
economic impact of $138.6 million in
income and 2,083 jobs for the Pacific
Coast groundfish fishery as a whole,
assuming no fishery effort substitutions
to offset losses. For the low impact
(December only closure) scenario, the
Analysis estimates the impact to be
losses of $24.6 million in income and
349 jobs.
Whether or not there will be an
economic impact of a closure depends
upon the likelihood that a closure
would occur. Since 2002, when the
West Coast Groundfish Observer
Program (WCGOP) first began
monitoring the groundfish fishery, the
whiting sector (including the at-sea,
shorebased, and tribal components) has
taken more than 11,000 Chinook in two
years, in 2005 and in 2014. In the nonwhiting sector, the bottom trawl fleet
takes the majority of the salmon
bycatch. Since 2002, the bottom trawl
fleet has taken more than 5,500 Chinook
twice, in 2002 and 2003. Overall, over
the last 15 years, there has never been
a situation where both sectors exceeded
their guideline levels at the same time.
Therefore, NMFS believes that it is
unlikely that a closure would be
triggered. However, the closure
mechanisms are a term and condition of
the Biological Opinion and are,
therefore, included in this proposed
rule. Such a mechanism would serve to
limit impact on listed salmon in
extraordinary circumstances.
J. Modifications to Depth Restrictions
Within the Western CCA
This proposed action would modify
the allowed fishing depths from 20-fm
(37-m) to 40-fm (73-m) for the
commercial fixed gear fishery and the
recreational fishery inside the Western
Cowcod Conservation Area (CCA). This
action would also add new waypoints
approximating the 30-fm (55-m) and 40fm (73-m) depth contours around Santa
Barbara Island, San Nicolas Island,
Tanner Bank, and Cortes Bank, because
waypoints approximating these
contours do not exist at these depths
currently. Fisheries are allowed to
operate in areas shallower than the
depth limit. This proposed action is
intended to allow additional
opportunities for commercial fixed gear
and recreational vessels to target healthy
stocks (nearshore rockfish, shelf
rockfish, cabezon, kelp greenling,
California scorpionfish, and lingcod),
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while still closing the depths where the
overall density of cowcod is the greatest
to provide protections as the stock
continues to rebuild.
The Council originally established
two CCAs (Western and Eastern) in 2001
as area closures to promote cowcod
rebuilding. These area closures
prohibited fishing in the main portion of
cowcod’s depth range (overall
distribution 22 to 270-fm (40 to 494-m),
with the highest density from 100 to
130-fm (183 to 238-m)) to reduce
encounters and mortality to allow the
stock to rebuild more quickly. The
Western CCA encompasses 5,126-mi2
(13,276-km2) and is located in the
Southern California Bight south of Point
Conception. The CCA is also expected
to provide protections for bronzespotted
rockfish, a stock with similar life history
characteristics, habitat associations, and
vulnerability to fishing as cowcod.
Commercial landings of bronzespotted
dropped in the late 1980s and have
remained at low levels from 1990 to
present.
Under the current regulations, 40.4mi2 (104.6 km2) (or less than 1 percent
of the entire CCA) is open to fishing due
to the 20-fm (37-m) depth restriction. By
increasing the depth to a 40-fm (73-m)
depth restriction, this proposed rule
would increase the fishable area to
150.4- mi2 (389.5-km2).
In the 2009–10 biennial specifications
and management measures, the Council
recommended modifying the
recreational depth restrictions inside the
CCA to 30-fm (55-m). NMFS
disapproved this recommendation in
the final rule (76 FR 27508; May 11,
2011), because there was limited
information on the impacts of the
proposed action on cowcod, especially
juvenile cowcod, which could delay
rebuilding. NMFS also indicated that,
because the ACL for cowcod was low (4
mt at that time), any measures that
potentially increased cowcod mortality
required better information on potential
biological and economic effects. At the
time of NMFS’ disapproval, cowcod was
at 4.5 percent of unfished biomass with
a projected time to rebuild of 2071.
Since the 2009–10 disapproval, the
NWFSC conducted a new stock
assessment for cowcod (assessed in
2013). The 2013 assessment concluded
that the stock is rebuilding much more
quickly than anticipated under its
rebuilding plan. Cowcod is expected to
be rebuilt by 2020, assuming full
removal of the ACL, which is 48 years
ahead of the target end date for the
rebuilding plan. Over the past several
years, cowcod harvest has consistently
been far below the ACL (see Section C.6
of Appendix C of the Analysis). As
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discussed in section III (Management
Measures), C, entitled ‘‘Biennial Fishery
Allocations,’’ of this preamble, NMFS is
proposing to set the cowcod ACT at 6
mt for 2019–20.
The 2013 cowcod assessment
explored ecosystem interactions and
updated habitat preferences of juvenile
cowcod based on research published
since the previous full assessment in
2007. The stock assessment identified
young of the year fish as being
distributed between 52 and 277-m (28–
151-fm), with juveniles found slightly
deeper. NMFS survey data and recent
catch data from observed trips inside
the Western CCA encountered no
cowcod (juvenile or adult) within the
proposed depth openings (see Section
C.6 of Appendix C of the Analysis).
Overall, the proposed measure is not
expected to result in increased cowcod
encounters, because the highest
densities of cowcod are found outside of
the depths in which this measure would
allow commercial fixed gear and
recreational fishing. Additionally, the
proposed measure is not expected to
increase mortality for bronzespotted
rockfish, because this stock is found
between 41-fm (75-m) and 205-fm (375m), which is outside the depth range of
the proposed action.
The Council recommended this
measure because the additional data on
habitat usage from the 2013 stock
assessment, the improved cowcod stock
trajectory, and the higher ACT for
cowcod demonstrate that there would
be no adverse impacts expected for
cowcod from this action. The expected
benefits of this action for the
commercial and recreational fleets are
described separately below.
Commercial
This proposed action would allow
greater access to valuable and
underattained stocks in this remote area.
Recent commercial fixed gear fishing
effort has been very low within the
Western CCA due to limited
opportunities within the current depth
restrictions. The proposed depth
changes within the CCA would allow
greater access to deeper stocks and
would create an economic incentive for
vessels to make trips to the area. NMFS
expects that a modest increase in the
number of fixed gear vessels fishing in
this area may occur as a result of this
proposed action; however the
magnitude of increase is difficult to
quantify. A redistribution of depth of
catch is also expected as a result of the
increased depths available for fishing.
The effects on groundfish of any
increase in effort would be limited
through the existing 2-month trip limits
delineated in Table 2 (South) to part
660.330.
Recreational
This proposed action would allow
recreational fishing within the Western
CCA out to 40 fathoms (73 m). NMFS
expects this measure would increase the
catch of target stocks, including shelf
rockfish, bocaccio, deeper nearshore
rockfish, and lingcod. The proposed
action would also be expected to reduce
pressure on shallower nearshore
rockfish stocks by allowing access to
currently inaccessible desirable
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nearshore (i.e., copper rockfish) and
shelf rockfish (i.e., vermilion rockfish)
found in deeper waters.
NMFS expects that this action would
result in an increase in the number of
angler trips, and an increase in the
amount of recreational catch, and result
in a redistribution of depth of catch.
Allowing access to deeper depths inside
the Western CCA is expected to increase
the number of groundfish trips between
10 percent and 20 percent, particularly
out of Ventura and Los Angeles, given
the proximity of these ports to the
Western CCA (see Section C.7 of
Appendix C of the Analysis). This
would provide additional revenues to
charter boat crews in the form of fish
processing and tips.
K. Modification of Lingcod and
Sablefish Discard Mortality Rates
This rule proposes to modify the
discard mortality rates (DMRs) for
lingcod and sablefish used to debit IFQ
accounts in the Shorebased IFQ
Program. Currently, NMFS debits IFQ
accounts for 100 percent of all catch of
these stocks, regardless of survival after
discarding. The Council recommended
implementing lower discard mortality
rates for lingcod and sablefish to match
those endorsed by the SSC and used for
year-end groundfish catch accounting.
For many other stocks, the best
scientific information available does not
indicate discard survival rates high
enough to warrant consideration of a
survival credit. The DMRs in Table 18
reflect the best scientific information
available.
TABLE 18—PROPOSED DISCARD MORTALITY RATES FOR LINGCOD AND SABLEFISH
Stock
Lingcod .......................................................................................
Sablefish .....................................................................................
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a Applies
Proposed
DMR (percent)
Gear
Bottom trawl
Fixed gear a
Bottom trawl
Fixed gear a
...............................................................................
................................................................................
...............................................................................
................................................................................
50
7
50
20
to both pot and hook and line gear.
By providing IFQ participants with
discard survival credits for lingcod and
sablefish, this action better meets some
of the objectives of the IFQ program,
such as increased attainments of and
increased value of IFQ stocks, such as
Dover sole and thornyheads. In
addition, this action aligns DMRs with
those used in year-end catch
accounting, which creates consistency
in mortality estimates. This proposed
action would allow modest increases in
attainment of co-occurring target stocks,
and increase marketability and value of
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retained catch by eliminating the need
to retain small fish that are not
economically marketable or desirable.
Landings and mortality would be
expected to increase proportionally by
the amount of QP savings/gains the
credit would provide, which for
sablefish could be a gain of one-half the
bottom trawl discards (9–21 mt per year)
and four-fifths the fixed gear discards
(11–20 mt per year), which could be
converted into additional landings.
Therefore, the resulting gains in
landings of sablefish could be an extra
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5–11 mt for bottom trawl and 9–16 mt
for fixed gear, which would only be
about a 1 percent increase in total
coastwide IFQ mortality of this stock
(see Section C.5 of Appendix C of the
Analysis).
As described in Section C.5 of
Appendix C of the Analysis, overall,
this proposed action would not be
expected to result in substantial changes
to discarding behavior because there are
operational costs for discarding in terms
of labor time for sorting catch, extra
fishing time necessary to replace the
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discarded fish, as well as the potential
risk that further fishing will not result
in catching larger fish. However, the
resulting ‘‘savings’’ of trawl sablefish,
due to a decreased deduction for
discarded fish, could possibly increase
landings of co-occurring, underattained
stocks, such as Dover sole, shortspine
thornyheads, and longspine
thornyheads (see Section C.5 of
Appendix C of the Analysis). Although
this measure could increase attainment,
IFQ participants’ total fishing mortality
would continue to be managed to
individual and sector allocations, and
catch would be constrained by the total
ACL for each stock.
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L. Removal of IFQ Daily Vessel Limits
Under the Shorebased IFQ Program, a
quota share (QS) permit authorizes a
person or group to own QS. A QS
account is an account that contains QS
allocations registered to the QS permit
for IFQ and individual bycatch quota
(IBQ) stocks. At the beginning of each
calendar year, NMFS issues quota
pounds (QPs) to each QS account based
on the IFQ or IBQ sector allocation. For
QPs to cover catch (landings and
discards) by a vessel in the shorebased
IFQ program, the QS permit owner must
transfer QPs from the QS account to a
vessel account. Vessel limits in vessel
accounts restrict the amount of QPs that
any vessel can catch or hold. NMFS
calculates annual QP vessel limits,
which are a set percentage of the total
IFQ sector allocation based on formulas
set through Amendment 20 to the
PCGFMP. The annual vessel QP limit
restricts the amount of used and unused
QP in a vessel account during a fishing
year.
NMFS also sets daily vessel limits for
overfished stocks, which cap the
amount of overfished stock QPs any
vessel account can have available in
their account on a given day. The
Council and NMFS established daily
vessel limits to prevent a person from
acquiring additional QP from others
before those QP are needed. IFQ sector
allocations of some overfished stocks
are low, which creates a strong
incentive for hoarding of QP for these
stocks to cover unexpected high catch
events. This daily limit keeps QP of
overfished stocks on the market and
available for trading. The daily limits
are set equal to the control limits for
each stock, which limit the amount of
QS and IBQ that a person, individually
or collectively, may own or control.
Because daily limits are set at the level
of the QS control limits, they have no
effect on those who only use QP from
their own QS account.
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Amendment 20 to the PCGFMP
intended for daily limits to apply for
overfished stocks. This means that when
stocks are declared rebuilt, the daily
limit for that stock must be removed
through rulemaking. In the 2017–18
biennium, bocaccio (south),
darkblotched rockfish, and Pacific ocean
perch were declared rebuilt, so this
action proposes to remove the daily
limits for these stocks. However,
because the daily vessel limit has been
ineffective for keeping catch available
for trading, this rule proposes to
eliminate the daily limits for all stocks.
Thus, in addition to bocaccio (south),
darkblotched rockfish, and Pacific ocean
perch, this rule also proposed to remove
daily vessels limits for cowcod (south),
yelloweye rockfish, and Pacific halibut.
As explained in in Section C.5 of
Appendix C of the Analysis, there may
be strategies to circumvent the daily
vessel limit. First, vessel owners can
sign sales contracts in advance, but
delay transferring QP for a stock until a
vessel account’s unused QP drops below
the daily limit. Second, entities can
temporarily acquire trawl permits and
use them to establish a second vessel
account in which they can store QP.
There is also evidence that the daily
limit is not constraining for several
stocks. Table C–65 in the Analysis
indicates that for the remaining
overfished stocks and Pacific halibut,
from 2011 through 2017, there has been
only one instance of a vessel landing
more than the daily limit. For the
recently rebuilt stocks, there has
generally been at least one vessel
landing more than the daily limit each
year for Pacific ocean perch, but this has
rarely occurred for bocaccio and
darkblotched rockfish since the start of
the Shorebased IFQ Program. Because
the daily limits for the remaining
overfished stocks and for Pacific halibut
have not been constraining, NMFS
expects that eliminating this provision
would not have a measurable effect on
the fishery.
M. Removal of Automatic Authority for
Darkblotched Rockfish and Pacific
Ocean Perch Set-Asides for At-Sea
Sector
Amendment 21 to the PCGFMP (75
FR 60867; October 1, 2010) established
allocations for darkblotched rockfish
and Pacific ocean perch catch in the atsea sector (C/P and mothership sectors).
At that time, darkblotched rockfish and
Pacific ocean perch were overfished,
and the ACLs and fishery allocations for
these stocks were low. NMFS has
authority to take automatic action to
close the at-sea sector, if necessary, to
ensure that darkblotched rockfish and
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Pacific ocean perch stays below the
allocation. In recent years, both of the
at-sea sectors have exceeded their
allocations of darkblotched rockfish (the
C/P sector in 2011, and the mothership
sector in 2014). The latter resulted in an
emergency Council meeting, and NMFS
took emergency action to reopen the
fisheries (79 FR 67095; November 12,
2014). However, because the overall
attainment of the darkblotched rockfish
ACL had been low, the Council
recommended and NMFS approved
Amendment 21–3 to the PCGFMP (83
FR 757; January 8, 2018). Amendment
21–3 replaced the at-sea sector Pacific
ocean perch and darkblotched rockfish
allocations with sector-specific setasides with a reserve for the C/P and
mothership sectors. The allocation for
the at-sea sectors is a percentage of the
trawl allocation of each stock.
Set-asides are managed on an annual
basis unless there is a risk of catch
exceeding a harvest specification (ACL,
ACT, or HG) inseason, unforeseen
impact on another fishery, or
conservation concerns, in which case
inseason action may be taken.
Amendment 21–3 also included a
reserve, or buffer, for set-asides. The
buffer is an amount deducted from the
ACL as part of the process of
determining the fishery HG (which
serves as the basis of allocating between
trawl and nontrawl fisheries), and is
intended to account for higher than
expected incidental catch. The buffer for
darkblotched rockfish and Pacific ocean
perch was established under
Amendment 27 to the PCGFMP (82 FR
9634; February 7, 2017). NMFS has the
authority to close either at-sea sector if
it is projected to exceed its set-aside
value, taking into account the buffer, for
either darkblotched rockfish or Pacific
ocean perch.
Darkblotched rockfish and Pacific
ocean perch have both been declared
rebuilt. The proposed 2019–20 ACLs for
both stocks are higher, reflecting the
change in stock status. In addition,
because of the change in stock status,
there is currently no buffer proposed for
2019–20. Because of these changes,
darkblotched rockfish and Pacific ocean
perch would be managed as de facto
allocations for the at-sea sectors. This
proposed rule would remove NMFS’s
automatic authority to close either
sector if they exceed their set-aside
value for these stocks, so that they are
managed like all other at-sea set-asides
in the PCGFMP. The Analysis
demonstrates that the expected risk of
the at-sea sectors exceeding their setaside values for darkblotched rockfish
and Pacific ocean perch is low, due to
low overall attainment in the trawl
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sector in recent years. In addition,
because this proposed adjustment
would remove the risk of shutting down
the fishery after reaching the set aside,
it increases the likelihood that the at-sea
sectors could attain their Pacific whiting
allocation (see Section C.4 of Appendix
C of the Analysis).
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N. Continuation of Adaptive
Management Pass Through
Under the Amendment 20 Trawl
Rationalization Program, NMFS reserves
10 percent of the QS for each of the nonwhiting stocks (including halibut
individual bycatch quota) each year for
an adaptive management program.
While the Council has never used the
allocation for this purpose,
conceptually, an adaptive management
program could distribute the reserved
QP to fishery participants to address
adverse effects of the Shoreside IFQ
program, including impacts to
community or processor stability,
conservation concerns, or other effects.
NMFS could also distribute the reserved
QPs to facilitate new entrants to
participate in the groundfish fishery. To
date, the Council has not recommended
establishing an adaptive management
program. Therefore, NMFS has
distributed (passed through) these QP to
quota shareholders each fishing year in
proportion to their QS for each stock.
This rule proposes that NMFS will
continue to pass through the QP
reserved for the adaptive management
program until the Council recommends
an alternative use of adaptive
management program QP. This is an
administrative measure that would not
affect fishing opportunity and related
catch.
O. Modification of the Incidental
Lingcod Retention Ratio in the Salmon
Troll Fishery
This proposed action would adjust
the existing incidental retention ratio for
landing lingcod based on the number of
Chinook landed in the ocean salmon
troll fishery in the area north of 40° 10’
N. latitude. The purpose of the ratio is
to allow salmon trollers to retain
incidentally caught lingcod, but to
discourage lingcod targeting. Currently,
participants are allowed to retain 1
lingcod per 15 Chinook salmon plus 1
lingcod per trip, up to a trip limit of 10
lingcod, on a trip where any fishing
occurs within the nontrawl RCA. This
limit only applies when lingcod
retention is allowed. Vessels
participating in the ocean salmon troll
fishery must be equipped with a vessel
monitoring system (VMS) to retain
incidentally caught groundfish. This
proposed action would allow retention
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of 1 lingcod per 5 Chinook salmon plus
1 lingcod per trip, up to a trip limit of
10 lingcod, on a trip where any fishing
occurs within the RCA. For 2019–20,
the lingcod fishery is proposed to be
open year-round for the open access
groundfish fishery. The Council can
adjust the ratio of lingcod retention per
Chinook landed through inseason
adjustments, if necessary.
As Section C.9 of Appendix C of the
Analysis notes, this action would be the
first modification of the ratio since it
was implemented in 2009 (74 FR 9874;
March 6, 2009). The Council
recommended this measure because
there has been an increased rate of
lingcod encounters as Chinook harvest
opportunities have declined. This
increased encounter rate has resulted in
an increase in regulatory discards of
lingcod. This proposed action would
align the lingcod retention limit with
the true lingcod encounter rate in the
salmon troll fishery while continuing to
discourage lingcod targeting. Salmon
trollers would still to be subject to the
existing overall limit of 10 lingcod per
trip and the existing requirement to
have VMS in order to retain any
incidentally caught groundfish. NMFS
does not expect this proposed action
will create an incentive for salmon
trollers to target lingcod because these
vessels would still be restricted to an
overall limit of 10 lingcod per trip.
P. Administrative Actions
NMFS also proposes four minor
changes to the regulatory text to clarify
regulatory intent. NMFS proposes to
add big skate to the LEFG and OA fixed
gear fisheries trip limit tables, Table 2
North and Table 2 South to Part 660
Subpart E, and Table 3 North and Table
3 South to Part 660 Subpart F. Big skate
is not currently listed in the trip limit
table for either the LEFG or OA
fisheries, and as such is unlimited.
Adding it to the trip limit tables would
provide clarity on this existing
management measure.
This proposed rule would remove an
obsolete reference to halibut weight
provisions at § 660.333(c)(3). The
obsolete reference originally mirrored a
provision in California state regulations,
but the California Department of Fish
and Wildlife removed this provision
from state regulations in 2004.
This proposed rule would clarify the
application of Amendment 21–3 setaside management of darkblotched
rockfish and Pacific ocean perch for the
at-sea sector for both years of the
biennium in Tables 1b, 2b, 1d, and 2d
to part 660, subpart C.
Finally, this action would remove the
WCGOP priority sampling requirement
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for canary rockfish and bocaccio,
formerly overfished stocks that were
declared rebuilt, as requested by the
Council at their March 2017 meeting.
Under this requirement, observers are
required to count and weigh these fish
on a docked vessel prior to offloading.
This requirement was implemented to
prevent vessels from discarding
overfished stocks for which they may
have low QP at port prior to offload.
Under 50 CFR 660.60(c)(1), the Council
can modify the list of stocks subject to
this catch monitoring requirement as a
routine management measure. In March
2017, the Council recommended that
the priority sampling requirement be
removed for canary rockfish and
bocaccio because these stocks are now
rebuilt.
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
state, ‘‘the Secretary will develop tribal
allocations and regulations under this
paragraph in consultation with the
affected tribe(s) and, insofar as possible,
with tribal consensus.’’ The tribal
management measures in this proposed
rule have been developed following
these procedures. The 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
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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.
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
ten year projections for routinely
adjusted harvest specifications and
management measures. The ten year
projections were produced to evaluate
the impacts of the ongoing
implementation of harvest
specifications and management
measures and to evaluate the impacts of
the routine adjustments that are the
main component of each biennial cycle.
Therefore, the EA for the 2019–20 cycle
tiers from the 2015–16 EIS and focuses
on the harvest specifications and
management measures that were not
within the scope of the ten 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.
An initial regulatory flexibility
analysis (IRFA) was prepared for this
action, as required by section 603 of the
Regulatory Flexibility Act (RFA) (5
U.S.C. 603). The IRFA describes the
economic impact this proposed rule, if
adopted, would have on small entities.
A description of the action, why it is
being considered, and the legal basis for
this action is contained in the SUMMARY
section and at the beginning of the
SUPPLEMENTARY INFORMATION section of
the preamble. A summary of the IRFA
follows. A copy of the IRFA is available
from NMFS (see ADDRESSES).
When an agency proposes regulations,
the RFA requires the agency to prepare
and make available for public comment
an IRFA that describes the impact on
small businesses, non-profit enterprises,
local governments, and other small
entities. The IRFA is to aid the agency
in considering all reasonable regulatory
alternatives that would minimize the
economic impact on affected small
entities.
The RFA (5 U.S.C. 601 et seq.)
requires government agencies to assess
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the effects that regulatory alternatives
would have on small entities, defined as
any business/organization
independently owned and operated, not
dominant in its field of operation
(including its affiliates). A small
harvesting business has combined
annual receipts of $11 million 2 or less
for all affiliated operations worldwide.
A small fish-processing business is
one that employs 750 or fewer persons
for all affiliated operations worldwide.
NMFS is applying this standard to
catcher/processors (C/Ps) for the
purposes of this rulemaking, because
these vessels earn the majority of their
revenue from selling processed fish.
For marinas and charter/party boats, a
small business is one that has annual
receipts not in excess of $7.5 million. A
wholesale business servicing the fishing
industry is a small business if it
employs 100 or fewer persons on a fulltime, part-time, temporary, or other
basis, at all its affiliated operations
worldwide.
For the purposes of this rulemaking,
a nonprofit organization is determined
to be ‘‘not dominant in its field of
operation’’ if it is considered small
under one of the following Small
Business Administration (SBA) size
standards: environmental, conservation,
or professional organizations are
considered small if they have combined
annual receipts of $15 million or less,
and other organizations are considered
small if they have combined annual
receipts of $7.5 million or less. The RFA
defines small governmental
jurisdictions as governments of cities,
counties, towns, townships, villages,
school districts, or special districts with
populations of less than 50,000.
Description and estimate of the number
of small entities to which the rule
applies, and estimate of economic
impacts by entity size and industry
This proposed rule would regulate
businesses that participate in the
groundfish fishery. This rule would
directly affect commercial vessels in the
groundfish fisheries, trawl QS holders
and Pacific whiting catch history
2 On December 29, 2015, the National Marine
Fisheries Service (NMFS) issued a final rule
establishing a small business size standard of $11
million in annual gross receipts for all businesses
primarily engaged in the commercial fishing
industry (NAICS 11411) for Regulatory Flexibility
Act (RFA) compliance purposes only (80 FR 81194,
December 29, 2015; 50 CFR part 200). The $11
million standard became effective on July 1, 2016,
and after that date it is to be used in all NMFS rules
subject to the RFA. Id. at 81194. This NMFS rule
is to be used in place of the U.S. Small Business
Administration’s (SBA) current standards of $20.5
million, $5.5 million, and $7.5 million for the
finfish (NAICS 114111), shellfish (NAICS 114112),
and other marine fishing (NAICS 114119) sectors of
the U.S. commercial fishing industry, respectively.
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endorsed permit holders (which include
shorebased whiting processors), tribal
vessels, and charterboat vessels.
Additionally, a provision of this
proposed rule would regulate
commercial vessels in the salmon troll
fleet.
To determine the number of small
entities potentially affected by this rule,
NMFS reviewed analyses of fish ticket
data and limited entry permit data,
information on charterboat, tribal, and
open access fleets, available costearnings data developed by NWFSC,
and responses associated with the
permitting process for the Trawl
Rationalization Program where
applicants were asked if they
considered themselves a small business
based on SBA definitions. This rule
would primarily regulate businesses
that harvest groundfish.
Charter Operations
There were an estimated 287 active
Commercial Passenger Fishing Vessels
(charter boats) engaged in groundfish
fishing in California in 2017. In 2017, an
estimated 49 charter boats targeted
groundfish in Oregon. There is no
Oregon license or tracking of party
fishing (or ‘‘six pack’’) vessel businesses
that will also be impacted, however in
one week in August 2017, there were
285 boat trips targeting recreational
groundfish in Oregon; this number
includes the 49 charter vessels and is
the upper bound of the number of such
entities likely to be impacted in Oregon.
Similarly in Washington, the number of
party/charter vessels likely to be
impacted by the proposed rule was 182
in 2017. All 705 of these vessels are
likely to be impacted by changes in
recreational catch guidelines for
groundfish in their respective states.
Commercial Vessels
Groundfish
Entities that are not registered as
trusts, estates, governments, or nonprofits are assumed to earn the majority
of their revenue from commercial
fishing. There are 124 QS permit
owners, who collectively received 76.5
percent of the QP issued in 2018.
Limited entry groundfish vessels are
required to self-report size across all
affiliated entities; of the business who
earn the majority of their revenue from
commercial fishing, one self-reported as
large. This entity owns four groundfish
permits and one QS permit. 264 entities
owning 376 permits self-reported as
small. The average small entity owns 1.4
permits, with 30 small entities owning
between 3–6 permits each. Open access
groundfish vessel owners are assumed
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to earn the majority of their revenue
from fishing and would thus fall into
this Small Business Administration
definition. 186 non-limited entry vessels
harvested at least $10,000 worth of
groundfish in 2017; these are likely to
be impacted by the proposed rule. This
number is likely an upper bound, as
some entities may own more than one
vessel. However, these generally small
operations are assumed to be
independent entities; with the top three
vessels having coastwide (including
non-groundfish) revenues averaging
$585,000. Median revenues were
$37,000 per vessel.
In addition to benefits from increasing
ACLs in the harvest specifications,
several of the new management
measures contained in the proposed
rule are likely to benefit vessels.
Clarifications resulting from the stock
complex restructuring and updates to
Rockfish Conservation Area coordinates
may streamline management burden for
vessels. IFQ vessels are expected to
benefit from the removal of daily vessel
quota pounds, which did not appear to
constrain operations, but which did
account for some level of administrative
burden for quota pound account
managers. With the elimination of these
limits, managers will have greater
flexibility in moving and holding quota
pounds for the remaining overfished
species and halibut IBQ. These vessels
and vessel account operators may also
benefit somewhat from changes to the
discard mortality rates in the IFQ
program. Some of the non-trawl fixed
gear vessels are expected to benefit by
the modifications to the commercial
depths inside the Western Cowcod
Conservation area in California.
Salmon Trollers
The proposed rule primarily impacts
entities in the groundfish fishery.
However, one new management
measure included the proposed rule
will likely benefit vessels primarily
involved in the salmon troll fishery,
through a modification in the incidental
lingcod retention ratio in that fishery.
This modification reflects the increased
rate of lingcod encounters during
declining Chinook salmon harvest
seasons. This modification would allow
salmon trollers to retain and sell a larger
number of lingcod caught incidentally
when targeting salmon. The level of
activity varies substantially, with trips
ranging from 500 to over 5,500 in a year.
The subsector of the fleet expected to
benefit from the proposed rule is much
smaller, as historically a small
proportion has elected to land lingcod
within the previously allowed limits. In
order to land lingcod, the vessel would
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have to install VMS, which (among
other factors) likely deters salmon
trollers. Thus, this provision of the
proposed rule is likely to impact 3 of
220 vessels operating in California. In
Oregon, between 7 and 85 trollers have
landed lingcod, and in Washington
between 10 and 17 trollers have landed
lingcod. The proposed rule would
confer a small benefit to these 105
vessels, which landed lingcod on a
median of 1–2 trips, with vessels in the
90th percentile landing lingcod on 5
trips annually. This small positive
benefit is not expected to be a
substantial impact. A substantial
number of small entities in the overall
salmon troll fishery are not likely to be
impacted by the proposed rule.
QS Owners
Because the harvest specifications
process determines the amount of QP
available in the catch share (Shorebased
IFQ Program) sector, this proposed rule
will impact QS. Twenty-two nonwhiting QS permit owners are estimated
to be primarily engaged in seafood
product preparation and packaging,
based on holdings of first receiver
permit affiliation in the non-public West
Coast Region permits database.
According to the size standard
described above, three of the entities
that own three of these permits are
considered small. These small
processing entities were issued 1.7
percent of the non-whiting QP issued in
2018. Some of these small processing
entities also own groundfish permits,
which are required on both catcher
vessels and catcher processors, and
which would be regulated by the
proposed rule; three small entities
primarily engaged in seafood processing
own two groundfish permits. Thirty
groundfish vessel permits are owned by
seven entities that are considered large,
as estimated by NMFS using the
standard described above, and as
estimated by information regarding
ownership affiliation and self-reported
size on groundfish permits and first
receiver site license permits (selfreported using the standard described
above). Six of these seven large
processing entities were issued 10.2
percent of the non-whiting QP issued in
2018 across sixteen QS permits.
Governmental Jurisdictions
According to the public IFQ Account
database as of June 19, 2018, the City of
Monterey owns QS of ten stocks. The
U.S. Census estimates the population to
be 28,454 as of July 1, 2017, so would
be considered a small governmental
jurisdiction by the RFA standard noted
above. The City of Monterey received
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0.5 percent of the QP issued for 2018,
according to the public IFQ Account
database.
Not-for-Profits
According to the public IFQ Account
database, six not-for-profit organizations
own QS in the catch share program and
would thus be impacted by the trawl
sector allocation under this proposed
rule. Five of these would be considered
small by the definition noted above
(with 2016 annual receipts as reported
on IRS form 990 of $120–500 thousand
dollars), and one would be considered
large (with self-reported fiscal year 2017
receipts of $1.1 billion). Collectively,
the five small not-for-profit
organizations received 7.2 percent of the
non-whiting 3 QP issued in 2018, and
the large not-for-profit organization
received 0.5 percent. The large not-forprofit organization also owned four
limited entry trawl permits which
would be impacted by the management
measures of the rule.
Small Trusts
Eleven personal or family trusts/
estates owned QS permits and would
thus potentially be impacted by the
trawl sector allocation under this
proposed rule. All of these are assumed
to be smaller than the size standard
noted above. Collectively, these eight
small entities received 4.2 percent of the
non-whiting QP issued for 2018.
A description of any significant
alternatives to the proposed rule that
accomplish the stated objectives of
applicable statutes and that minimize
any significant economic impact of the
proposed rule on small entities
In the event of a fishery closure under
the Biological Opinion provisions
included in this rule (50 CFR
660.60(d)(1)(v) and (vi) of this proposed
rule), the loss of revenue in groundfish
fisheries would likely have a substantial
negative impact on a significant number
of small entities, and an equal impact on
all large entities in the fishery. However,
such a closure is not anticipated by
NMFS and the Council, given historic
catch levels and the existence of
cooperative management structures with
extensive inseason monitoring. Because
these provisions are non-discretionary
under the ESA, there are no significant
alternatives to the proposed rule that
would minimize adverse economic
impacts on small entities.
The Council considered alternatives
to the actions in this proposed rule that
3 Whiting is issued annually through a separate
rulemaking process resulting from international
treaty negotiations. (See 83 FR 22401 for more
information and 2018 allocations.)
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would have a lower level of benefits to
small entities. The Council did not
consider alternatives that would have
greater benefits to small entities, as
these would not have met several
primary objectives of the rule (the
prevention of overfishing, the rebuilding
of overfished stocks, and ensuring
conservation).
Under the No Action alternative, the
default harvest specifications and
associated routine management
measures would be implemented using
best scientific information available to
establish default harvest control rules
for all groundfish stocks. The Council
considered alternative specifications for
California scorpionfish, lingcod north of
40°10’ N lat, and yelloweye rockfish. In
each case, the Council selected the
harvest control rule that resulted in the
maximum benefits to both large and
small directly regulated entities.
Routine management measures are
adjusted according to harvest
specifications, which also impact the
new management measures available for
implementation.
Regulatory Flexibility Act (RFA)
Determination of No Significant Impact
The RFA requires Federal agencies to
conduct an analysis of the impact of the
proposed rule on small entities. The
proposed rule would impact a
significant number of small entities, but
that these impacts are expected to range
from neutral to positive, depending on
individual response to increased harvest
guidelines and updated management
measures. Because there are no
anticipated compliance costs or other
adverse effects, NMFS concludes
(subject to review of any pertinent
public comments) that the rule will not
have a substantial adverse impact on the
significant number of directly regulated
entities.
List of Subjects in 50 CFR Part 660
Fisheries, Fishing, Reporting and
recordkeeping requirements.
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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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*
*
General definitions.
*
*
*
Conservation Area(s) * * *
(1) Groundfish Conservation Area or
GCA means a geographic area defined
by coordinates expressed in degrees
latitude and longitude, wherein fishing
by a particular gear type or types may
be prohibited. Regulations at
§ 660.60(c)(3) describe the various
purposes for which these GCAs may be
implemented. Regulations at § 660.70
define coordinates for these polygonal
GCAs: Yelloweye Rockfish Conservation
Areas, Cowcod Conservation Areas,
waters encircling the Farallon Islands,
and waters encircling the Cordell Bank.
GCAs also include Bycatch Reduction
Areas (BRAs), and Rockfish
Conservation Areas or RCAs, which are
areas closed to fishing by particular gear
types, bounded by lines approximating
particular depth contours. RCA
boundaries may and do change
seasonally according to conservation
needs. Regulations at §§ 660.70 through
660.74 define boundary lines with
latitude/longitude coordinates;
regulations at Tables 1 (North) and 1
(South) of subpart D, Tables 2 (North)
and 2 (South) of subpart E, and Tables
3 (North) and 3 (South) of subpart F set
seasonal boundaries. Fishing
prohibitions associated with GCAs are
in addition to those associated with EFH
Conservation Areas.
*
*
*
*
*
*
For the reasons set out in the
preamble, 50 CFR part 660 is proposed
to be amended as follows:
18:17 Sep 18, 2018
§ 660.11
Groundfish * * *
Dated: September 4, 2018.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
VerDate Sep<11>2014
2. In § 660.11:
a. In the definition of ‘‘Conservation
area(s)’’, revise paragraph (1); and
■ b. In the definition of ‘‘Groundfish’’:
■ i. Revise paragraphs (6) and (7)(i)
introductory text;
■ ii. Redesignate paragraph (7)(i)(B) as
(7)(i)(C);
■ iii. Add new paragraph (7)(i)(B); and
■ iv. Revise paragraph (9).
The revisions and additions read as
follows:
■
■
*
*
*
*
(6) Roundfish: Cabezon,
Scorpaenichthys marmoratus; kelp
greenling, Hexagrammos decagrammus;
lingcod, Ophiodon elongatus; Pacific
cod, Gadus macrocephalus; Pacific
whiting, Merluccius productus;
sablefish, Anoplopoma fimbria. Species
listed below with an area-specific listing
are managed within a complex in that
area-specific listing.
(i) Between 46°16′ N lat. and the U.S.
Canada border (Washington): Cabezon,
S. marmoratus and kelp greenling, H.
decagrammus.
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(ii) Between 46°16′ N lat. and 42° N
lat. (Oregon): Cabezon, S. marmoratus
and kelp greenling, H. decagrammus.
(7) * * *
(i) Nearshore rockfish includes black
rockfish, Sebastes melanops (off
Washington) and the following
nearshore rockfish species managed in
‘‘minor rockfish’’ complexes:
*
*
*
*
*
(B) Between 46°16′ N lat. and 42° N
lat. (Oregon): black rockfish, S.
melanops, blue rockfish, S. mystinus,
deacon rockfish, S. diaconus.
*
*
*
*
*
(9) ‘‘Other Fish’’: kelp greenling
(Hexagrammos decagrammus) off
California and leopard shark (Trakis
semifasciata).
*
*
*
*
*
■ 3. Amend § 660.40 as follows:
■ a. Remove paragraphs (a), (c), and (d);
■ b. Redesignate paragraph (b) as
paragraph (a), and paragraph (e) as
paragraph (b); and
■ c. Revise newly redesignated
paragraph (b).
The revision reads as follows:
§ 660.40
plans.
Overfished species rebuilding
*
*
*
*
*
(b) Yelloweye rockfish. Yelloweye
rockfish was declared overfished in
2002. The target year for rebuilding the
yelloweye rockfish stock to BMSY is
2029. The harvest control rule to be
used to rebuild the yelloweye rockfish
stock is an annual SPR harvest rate of
65.0 percent.
■ 4. In § 660.50, revise paragraphs
(f)(2)(ii) and (f)(6) and add paragraph (h)
to read as follows:
§ 660.50 Pacific Coast treaty Indian
fisheries.
*
*
*
*
*
(f) * * *
(2) * * *
(ii) The Tribal allocation is 561 mt in
2019 and 572 mt in 2020 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 1.5 percent for
estimated discard mortality.
*
*
*
*
*
(6) Petrale sole. For petrale sole, treaty
fishing vessels are restricted to a
fleetwide harvest target of 290 mt each
year.
*
*
*
*
*
(h) Salmon bycatch. This fishery may
be closed through automatic action at
660.60(d)(1)(v) and (d)(1)(vi).
■ 5. In § 660.55, revise paragraphs
(c)(1)(i)(A) and (B) to read as follows:
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§ 660.55
Allocations.
*
*
*
*
*
(c) * * *
(1) * * *
(i) * * *
(A) Darkblotched rockfish. Distribute
9 percent or 25 mt, whichever is greater,
of the total trawl allocation of
darkblotched rockfish to the Pacific
whiting fishery (MS sector, C/P sector,
and Shorebased IFQ sectors). The
distribution of darkblotched rockfish to
each sector will be done pro rata relative
to the sector’s allocation of the
commercial harvest guideline for Pacific
whiting. Darkblotched rockfish
distributed to the MS sector and C/P
sector are managed as set-asides at Table
1d and Table 2d, subpart C. The
allocation of darkblotched rockfish to
the Pacific whiting IFQ fishery
contributes to the Shorebased IFQ
allocation. After deducting allocations
for the Pacific whiting fishery, the
remaining trawl allocation is allocated
to the Shorebased IFQ Program.
(B) Pacific Ocean Perch (POP).
Distribute 17 percent or 30 mt,
whichever is greater, of the total trawl
allocation of POP to the Pacific whiting
fishery (MS sector, C/P sector, and
Shorebased IFQ sector). The distribution
of POP to each sector will be done pro
rata relative to the sector’s allocation of
the commercial harvest guideline for
Pacific whiting. POP distributed to the
MS sector and C/P sector are managed
as set-asides at Table 1d and Table 2d,
subpart C. The allocation of POP to the
Pacific whiting IFQ fishery contributes
to the Shorebased IFQ allocation. After
deducting allocations for the Pacific
whiting fishery, the remaining trawl
allocation is allocated to the Shorebased
IFQ Program.
*
*
*
*
*
■ 6. Amend § 660.60 as follows:
■ a. Revise paragraph (d)(1)(v);
■ b. Remove paragraph (d)(1)(vii);
■ c. Redesignate paragraph (d)(1)(vi) as
paragraph (d)(1)(vii); and
■ d. Add new paragraph (d)(1)(vi).
The revision and addition read as
follows:
§ 660.60 Specifications and management
measures.
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*
*
*
*
*
(d) * * *
(1) * * *
(v) Close one or both of the whiting
or non-whiting sectors of the groundfish
fishery upon that sector having
exceeded its annual Chinook salmon
bycatch guideline and the reserve. The
whiting sector includes the Pacific
whiting IFQ fishery, MS, and C/P
sectors. The non-whiting sector includes
the midwater trawl, bottom trawl, and
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fixed gear fisheries under the
Shorebased IFQ Program, limited entry
fixed gear fisheries, open access
fisheries, and recreational fisheries
subject to this provision as set out in
§ 660.360(d).
(A) The whiting sector Chinook
salmon bycatch guideline is 11,000 fish.
(B) The non-whiting sector Chinook
salmon bycatch guideline is 5,500 fish.
(C) The reserve is 3,500 fish.
(vi) Close the whiting or non-whiting
sector of the groundfish fishery upon
that sector having exceeded its annual
Chinook salmon bycatch guideline if the
other sector has already been closed
after exceeding its Chinook salmon
bycatch guideline and the reserve. The
whiting sector includes the Pacific
whiting IFQ fishery, MS, and C/P
sectors. The non-whiting sector includes
the midwater trawl, bottom trawl, and
fixed gear fisheries under the
Shorebased IFQ Program, limited entry
fixed gear fisheries, open access
fisheries, and recreational fisheries
subject to this provision as set out in
§ 660.360(d).
*
*
*
*
*
■ 7. Amend § 660.71 as follows:
■ a. Redesignate paragraphs (k) through
(n) as paragraphs (o) through (r); and
■ b. Add new paragraphs (k) through (n)
and paragraphs (s) through (v).
The additions read as follows:
§ 660.71 Latitude/longitude coordinates
defining the 10-fm (18-m) through 40-fm (73m) depth contours.
*
*
*
*
*
(k) The 30 fm (55 m) depth contour
around Santa Barbara Island off the state
of California is defined by straight lines
connecting all of the following points in
the order stated:
(1) 33°30.38′ N lat., 119°03.15′ W
long.;
(2) 33°29.64′ N lat., 119°00.58′ W
long.;
(3) 33°27.24′ N lat., 119°01.73′ W
long.;
(4) 33°27.76′ N lat., 119°03.48′ W
long.;
(5) 33°29.50′ N lat., 119°04.20′ W
long.; and
(6) 33°30.38′ N lat., 119°03.15′ W
long.
(l) The 30 fm (55 m) depth contour
around San Nicholas Island off the state
of California is defined by straight lines
connecting all of the following points in
the order stated:
(1) 33°18.39′ N lat., 119°38.87′ W
long.;
(2) 33°18.63′ N lat., 119°27.52′ W
long.;
(3) 33°15.24′ N lat., 119°20.10′ W
long.;
(4) 33°13.27′ N lat., 119°20.10′ W
long.;
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47439
(5) 33°12.16′ N lat., 119°26.82′ W
long.;
(6) 33°13.20′ N lat., 119°31.87′ W
long.;
(7) 33°15.70′ N lat., 119°38.87′ W
long.;
(8) 33°17.52′ N lat., 119°40.15′ W
long.; and
(9) 33°18.39′ N lat., 119°38.87′ W
long.
(m) The 30 fm (55 m) depth contour
around Tanner Bank off the state of
California is defined by straight lines
connecting all of the following points in
the order stated:
(1) 32°43.02′ N lat., 119°08.52′ W
long.;
(2) 32°41.81′ N lat., 119°06.20′ W
long.;
(3) 32°40.67′ N lat., 119°06.82′ W
long.;
(4) 32°41.62′ N lat., 119°09.46′ W
long.; and
(5) 32°43.02′ N lat., 119°08.52′ W
long.
(n) The 30 fm (55 m) depth contour
around Cortes Bank off the state of
California is defined by straight lines
connecting all of the following points in
the order stated:
(1) 32°29.73′ N lat., 119°12.95′ W
long.;
(2) 32°28.17′ N lat., 119°07.04′ W
long.;
(3) 32°26.27′ N lat., 119°04.14′ W
long.;
(4) 32°25.22′ N lat., 119°04.77′ W
long.;
(5) 32°28.60′ N lat., 119°14.15′ W
long.; and
(6) 32°29.73′ N lat., 119°12.95′ W
long.
*
*
*
*
*
(s) The 40 fm (73 m) depth contour
around Santa Barbara Island off the state
of California is defined by straight lines
connecting all of the following points in
the order stated:
(1) 33°30.87′ N lat., 119°02.43′ W
long.;
(2) 33°29.87′ N lat., 119°00.34′ W
long.;
(3) 33°27.08′ N lat., 119°01.65′ W
long.;
(4) 33°27.64′ N lat., 119°03.45′ W
long.;
(5) 33°29.12′ N lat., 119°04.55′ W
long.;
(6) 33°29.66′ N lat., 119°05.49′ W
long.; and
(7) 33°30.87′ N lat., 119°02.43′ W
long.
(t) The 40 fm (73 m) depth contour
around Tanner Bank off the state of
California is defined by straight lines
connecting all of the following points in
the order stated:
(1) 32°43.40′ N lat., 119°08.56′ W
long.;
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(2) 32°41.36′ N lat., 119°05.02′ W
long.;
(3) 32°40.07′ N lat., 119°05.59′ W
long.;
(4) 32°41.51′ N lat., 119°09.76′ W
long.; and
(5) 32°43.40′ N lat., 119°08.56′ W
long.
(u) The 40 fm (73 m) depth contour
around San Nicholas Island off the state
of California is defined by straight lines
connecting all of the following points in
the order stated:
(1) 33°19.30′ N lat., 119°41.05′ W
long.;
(2) 33°19.42′ N lat., 119°27.88′ W
long.;
(3) 33°14.31′ N lat., 119°17.48′ W
long.;
(4) 33°12.90′ N lat., 119°17.64′ W
long.;
(5) 33°11.89′ N lat., 119°27.26′ W
long.;
(6) 33°12.19′ N lat., 119°29.96′ W
long.;
(7) 33°15.42′ N lat., 119°39.14′ W
long.;
(8) 33°17.58′ N lat., 119°41.38′ W
long.; and
(9) 33°19.30′ N lat., 119°41.05′ W
long.
(v) The 40 fm (73 m) depth contour
around Cortes Bank off the state of
California is defined by straight lines
connecting all of the following points in
the order stated:
(1) 32°30.00′ N lat., 119°12.98′ W
long.;
(2) 32°28.33′ N lat., 119°06.81′ W
long.;
(3) 32°25.69′ N lat., 119°03.21′ W
long.;
(4) 32°24.66′ N lat., 119°03.83′ W
long.;
(5) 32°28.48′ N lat., 119°14.66′ W
long.; and
(6) 32°30.00′ N lat., 119°12.98′ W
long.
■ 8. Amend § 660.72 as follows:
■ a. Redesignate paragraphs (k)(15)
through (31) as (k)(17) through (33),
respectively; and
■ b. Add new paragraphs (k)(15) and
(16).
The additions read as follows:
§ 660.72 Latitude/longitude coordinates
defining the 50 fm (91 m) through 75 fm (137
m) depth contours.
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*
*
*
*
*
(k) * * *
(15) 33°57.77′ N lat., 119°33.49′ W
long.;
(16) 33°57.64′ N lat., 119°35.78′ W
long.;
*
*
*
*
*
■ 9. Amend § 660.73 as follows:
■ a. Revise paragraphs (a)(178), (a)(181),
(a)(190) through (192), and (d)(205)
through (354);
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18:17 Sep 18, 2018
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b. Add paragraphs (d)(355) through
(363);
■ c. Revise paragraphs (h)(281) through
(313); and
■ d. Add paragraphs (h)(314) through
(316).
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) * * *
(178) 40°10.13′ N lat., 124°21.92′ W
long.;
*
*
*
*
*
(181) 40°06.39′ N lat., 124°17.26′ W
long.;
*
*
*
*
*
(190) 40°01.00′ N lat., 124°09.96′ W
long.;
(191) 39°58.07′ N lat., 124°11.81′ W
long.;
(192) 39°56.39′ N lat., 124°08.69′ W
long.;
*
*
*
*
*
(d) * * *
(205) 40°02.67′ N lat., 124°11.83′ W
long.;
(206) 40°02.70′ N lat., 124°10.57′ W
long.;
(207) 40°04.08′ N lat., 124°10.09′ W
long.;
(208) 40°04.08′ N lat., 124°09.10′ W
long.;
(209) 40°01.23′ N lat., 124°08.91′ W
long.;
(210) 40°01.18′ N lat., 124°09.92′ W
long.;
(211) 39°58.05′ N lat., 124°11.87′ W
long.;
(212) 39°56.39′ N lat., 124°08.70′ W
long.;
(213) 39°54.64′ N lat., 124°07.31′ W
long.;
(214) 39°53.87′ N lat., 124°07.95′ W
long.;
(215) 39°52.42′ N lat., 124°08.18′ W
long.;
(216) 39°49.64′ N lat., 124°06.05′ W
long.;
(217) 39°49.30′ N lat., 124°04.60′ W
long.;
(218) 39°48.49′ N lat., 124°03.86′ W
long.;
(219) 39°47.73′ N lat., 124°04.59′ W
long.;
(220) 39°42.50′ N lat., 124°00.60′ W
long.;
(221) 39°34.23′ N lat., 123°56.82′ W
long.;
(222) 39°33.00′ N lat., 123°56.44′ W
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long.;
(224) 39°31.34′ N lat., 123°56.71′ W
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(227) 39°05.56′ N lat., 123°57.24′ W
long.;
(228) 39°01.75′ N lat., 123°56.83′ W
long.;
(229) 38°59.52′ N lat., 123°55.95′ W
long.;
(230) 38°58.98′ N lat., 123°56.57′ W
long.;
(231) 38°57.50′ N lat., 123°56.57′ W
long.;
(232) 38°53.91′ N lat., 123°56.00′ W
long.;
(233) 38°42.57′ N lat., 123°46.60′ W
long.;
(234) 38°28.72′ N lat., 123°35.61′ W
long.;
(235) 38°28.01′ N lat., 123°36.47′ W
long.;
(236) 38°20.94′ N lat., 123°31.26′ W
long.;
(237) 38°15.94′ N lat., 123°25.33′ W
long.;
(238) 38°10.95′ N lat., 123°23.19′ W
long.;
(239) 38°05.52′ N lat., 123°22.90′ W
long.;
(240) 38°08.46′ N lat., 123°26.23′ W
long.;
(241) 38°06.95′ N lat., 123°28.03′ W
long.;
(242) 38°06.25′ N lat., 123°29.70′ W
long.;
(243) 38°04.57′ N lat., 123°31.37′ W
long.;
(244) 38°02.32′ N lat., 123°31.09′ W
long.;
(245) 37°59.97′ N lat., 123°28.43′ W
long.;
(246) 37°58.10′ N lat., 123°26.69′ W
long.;
(247) 37°55.46′ N lat., 123°27.05′ W
long.;
(248) 37°51.51′ N lat., 123°24.86′ W
long.;
(249) 37°45.01′ N lat., 123°12.09′ W
long.;
(250) 37°35.67′ N lat., 123°01.56′ W
long.;
(251) 37°26.62′ N lat., 122°56.21′ W
long.;
(252) 37°14.41′ N lat., 122°49.07′ W
long.;
(253) 37°11.00′ N lat., 122°45.87′ W
long.;
(254) 37°07.00′ N lat., 122°41.97′ W
long.;
(255) 37°03.19′ N lat., 122°38.31′ W
long.;
(256) 37°00.99′ N lat., 122°35.51′ W
long.;
(257) 36°58.31′ N lat., 122°27.56′ W
long.;
(258) 37°00.54′ N lat., 122°24.74′ W
long.;
(259) 36°57.81′ N lat., 122°24.65′ W
long.;
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(260) 36°58.54′ N lat., 122°21.67′ W
long.;
(261) 36°56.52′ N lat., 122°21.70′ W
long.;
(262) 36°55.37′ N lat., 122°18.45′ W
long.;
(263) 36°52.16′ N lat., 122°12.17′ W
long.;
(264) 36°51.53′ N lat., 122°10.67′ W
long.;
(265) 36°48.05′ N lat., 122°07.59′ W
long.;
(266) 36°47.35′ N lat., 122°03.27′ W
long.;
(267) 36°50.71′ N lat., 121°58.17′ W
long.;
(268) 36°48.89′ N lat., 121°58.90′ W
long.;
(269) 36°47.70′ N lat., 121°58.76′ W
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(270) 36°48.37′ N lat., 121°51.15′ W
long.;
(271) 36°45.74′ N lat., 121°54.18′ W
long.;
(272) 36°45.50′ N lat., 121°57.73′ W
long.;
(273) 36°44.02′ N lat., 121°58.55′ W
long.;
(274) 36°38.84′ N lat., 122°01.32′ W
long.;
(275) 36°35.63′ N lat., 122°00.98′ W
long.;
(276) 36°32.47′ N lat., 121°59.17′ W
long.;
(277) 36°32.52′ N lat., 121°57.62′ W
long.;
(278) 36°30.16′ N lat., 122°00.55′ W
long.;
(279) 36°24.56′ N lat., 121°59.19′ W
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(280) 36°22.19′ N lat., 122°00.30′ W
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(281) 36°20.62′ N lat., 122°02.93′ W
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(282) 36°18.89′ N lat., 122°05.18′ W
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(283) 36°14.45′ N lat., 121°59.44′ W
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(284) 36°13.73′ N lat., 121°57.38′ W
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(285) 36°14.41′ N lat., 121°55.45′ W
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(286) 36°10.25′ N lat., 121°43.08′ W
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(287) 36°07.67′ N lat., 121°40.92′ W
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(288) 36°02.51′ N lat., 121°36.76′ W
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(289) 36°01.04′ N lat., 121°36.68′ W
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(290) 36°00.00′ N lat., 121°35.15′ W
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(291) 35°57.84′ N lat., 121°33.10′ W
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(292) 35°45.57′ N lat., 121°27.26′ W
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(294) 35°25.92′ N lat., 121°05.52′ W
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(296) 35°07.60′ N lat., 120°56.49′ W
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(297) 34°57.77′ N lat., 120°53.87′ W
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(298) 34°42.30′ N lat., 120°53.42′ W
long.;
(299) 34°37.69′ N lat., 120°50.04′ W
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(300) 34°30.13′ N lat., 120°44.45′ W
long.;
(301) 34°27.00′ N lat., 120°39.24′ W
long.;
(302) 34°24.71′ N lat., 120°35.37′ W
long.;
(303) 34°21.63′ N lat., 120°24.86′ W
long.;
(304) 34°24.39′ N lat., 120°16.65′ W
long.;
(305) 34°22.48′ N lat., 119°56.42′ W
long.;
(306) 34°18.54′ N lat., 119°46.26′ W
long.;
(307) 34°16.37′ N lat., 119°45.12′ W
long.;
(308) 34°15.91′ N lat., 119°47.29′ W
long.;
(309) 34°13.80′ N lat., 119°45.40′ W
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(310) 34°11.69′ N lat., 119°41.80′ W
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(311) 34°09.98′ N lat., 119°31.87′ W
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(312) 34°08.12′ N lat., 119°27.71′ W
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(313) 34°06.35′ N lat., 119°32.65′ W
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(314) 34°06.80′ N lat., 119°40.08′ W
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(315) 34°07.48′ N lat., 119°47.54′ W
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(316) 34°08.21′ N lat., 119°54.90′ W
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(317) 34°06.85′ N lat., 120°05.60′ W
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(318) 34°07.03′ N lat., 120°10.47′ W
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(319) 34°08.77′ N lat., 120°18.46′ W
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(320) 34°11.89′ N lat., 120°28.09′ W
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(321) 34°12.53′ N lat., 120°29.82′ W
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(322) 34°09.02′ N lat., 120°37.47′ W
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(323) 34°01.01′ N lat., 120°31.17′ W
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(324) 33°58.07′ N lat., 120°28.33′ W
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(325) 33°53.37′ N lat., 120°14.43′ W
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(326) 33°50.53′ N lat., 120°07.20′ W
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(327) 33°45.88′ N lat., 120°04.26′ W
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(330) 33°42.36′ N lat., 119°49.60′ W
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(332) 33°55.99′ N lat., 119°41.40′ W
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(333) 33°58.48′ N lat., 119°27.90′ W
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(334) 33°59.24′ N lat., 119°23.61′ W
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(335) 33°59.35′ N lat., 119°21.71′ W
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(336) 33°59.94′ N lat., 119°19.57′ W
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(337) 34°04.48′ N lat., 119°15.32′ W
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(338) 34°02.80′ N lat., 119°12.95′ W
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(339) 34°02.39′ N lat., 119°07.17′ W
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(340) 34°03.75′ N lat., 119°04.72′ W
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(341) 34°01.82′ N lat., 119°03.24′ W
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(342) 33°59.33′ N lat., 119°03.49′ W
long.;
(343) 33°59.01′ N lat., 118°59.56′ W
long.;
(344) 33°59.51′ N lat., 118°57.25′ W
long.;
(345) 33°58.83′ N lat., 118°52.50′ W
long.;
(346) 33°58.55′ N lat., 118°41.86′ W
long.;
(347) 33°55.10′ N lat., 118°34.25′ W
long.;
(348) 33°54.30′ N lat., 118°38.71′ W
long.;
(349) 33°50.88′ N lat., 118°37.02′ W
long.;
(350) 33°39.78′ N lat., 118°18.40′ W
long.;
(351) 33°35.50′ N lat., 118°16.85′ W
long.;
(352) 33°32.46′ N lat., 118°10.90′ W
long.;
(353) 33°34.11′ N lat., 117°54.07′ W
long.;
(354) 33°31.61′ N lat., 117°49.30′ W
long.;
(355) 33°16.36′ N lat., 117°35.48′ W
long.;
(356) 33°06.81′ N lat., 117°22.93′ W
long.;
(357) 32°59.28′ N lat., 117°19.69′ W
long.;
(358) 32°55.37′ N lat., 117°19.55′ W
long.;
(359) 32°53.35′ N lat., 117°17.05′ W
long.;
(360) 32°53.36′ N lat., 117°19.12′ W
long.;
(361) 32°46.42′ N lat., 117°23.45′ W
long.;
(362) 32°42.71′ N lat., 117°21.45′ W
long.; and
(363) 32°34.54′ N lat., 117°23.04′ W
long.
*
*
*
*
*
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(281) 34°07.10′ N lat., 120°10.37′ W
long.;
(282) 34°11.07′ N lat., 120°25.03′ W
long.;
(283) 34°09.00′ N lat., 120°18.40′ W
long.;
(284) 34°13.16′ N lat., 120°29.40′ W
long.;
(285) 34°09.41′ N lat., 120°37.75′ W
long.;
(286) 34°03.15′ N lat., 120°34.71′ W
long.;
(287) 33°57.09′ N lat., 120°27.76′ W
long.;
(288) 33°51.00′ N lat., 120°09.00′ W
long.;
(289) 33°38.16′ N lat., 119°59.23′ W
long.;
(290) 33°37.04′ N lat., 119°50.17′ W
long.;
(291) 33°42.28′ N lat., 119°48.85′ W
long.;
(292) 33°53.96′ N lat., 119°53.77′ W
long.;
(293) 33°55.88′ N lat., 119°41.05′ W
long.;
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(295) 33°59.26′ N lat., 119°21.92′ W
long.;
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(297) 34°03.12′ N lat., 119°15.51′ W
long.;
(298) 34°01.97′ N lat., 119°07.28′ W
long.;
(299) 34°03.60′ N lat., 119°04.71′ W
long.;
(300) 33°59.30′ N lat., 119°03.73′ W
long.;
(301) 33°58.87′ N lat., 118°59.37′ W
long.;
(302) 33°58.08′ N lat., 118°41.14′ W
long.;
(303) 33°50.93′ N lat., 118°37.65′ W
long.;
(304) 33°39.54′ N lat., 118°18.70′ W
long.;
(305) 33°35.42′ N lat., 118°17.14′ W
long.;
(306) 33°32.15′ N lat., 118°10.84′ W
long.;
(307) 33°33.71′ N lat., 117°53.72′ W
long.;
(308) 33°31.17′ N lat., 117°49.11′ W
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(310) 33°06.77′ N lat., 117°22.92′ W
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long.;
(312) 32°55.83′ N lat., 117°20.15′ W
long.;
(313) 32°46.29′ N lat., 117°23.89′ W
long.;
(314) 32°42.00′ N lat., 117°22.16′ W
long.;
(315) 32°39.47′ N lat., 117°27.78′ W
long.; and
(316) 32°34.83′ N lat., 117°24.69′ W
long.
*
*
*
*
*
■ 10. Tables 1a to part 660, subpart C
through 1d to part 660, subpart C are
revised to read as follows:
Sec.
*
*
*
*
*
Table 1a to Part 660, Subpart C—2019,
Specifications of OFL, ABC, ACL, ACT
and Fishery HG (Weights in Metric Tons)
Table 1b. to Part 660, Subpart C—2019,
Allocations by Species or Species Group
(Weight in Metric Tons)
Table 1c. to Part 660, Subpart C—Sablefish
North of 36° N lat. Allocations, 2019
Table 1d. to Part 660, Subpart C—At-Sea
Whiting Fishery Annual Set-Asides,
2019
*
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Table la to Part 660, Subpart C-2019, Specifications of OFL, ABC, ACL, ACT and
Fishery HG (Weights in Metric Tons)
Black Rockfish g/
Black Rockfish h/
Bocaccio i/
Cabezonj/
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California Scorpionfish k/
Canary Rockfish 11
Chili pepper Rockfish m/
Darkblotched Rockfish n/
Dover Sole o/
English Sole p/
Lingcod q/
Lingcod r/
Longnose Skate s/
Longspine Thornyhead t/
Longspine Thornyhead u/
Pacific Cod v/
Pacific Whiting w/
Pacific Ocean Perch x/
Petrale Soley/
Area
S. of 40°10' N. lat.
(Conception)
(Monterey)
Coastwide
Coastwide
Coastwide
California (S. of 42° N.
lat.)
Washington (N. of 46° 16'
N. lat.)
S. of 40°10' N. lat.
California (S. of 42° N.
lat.)
S. of34°27' N. lat.
Coastwide
S. of 40°10' N. lat.
Coastwide
Coastwide
Coastwide
N. of 40°10' N. lat.
S. of 40°10' N. lat.
Coastwide
N. of 34 °27' N. lat.
S. of34°27' N. lat.
Coastwide
Coastwide
N. of 40°10' N lat.
Coastwide
Sablefish z/
N. of36° N. lat.
Sablefish aa/
Shortbelly Rockfish bb/
Shortspine Thornyhead cc/
Shortspine Thornyhead dd/
S. of 36° N. lat
Coastwide
N. of 34 °27' N. lat.
S. of34°27' N. lat.
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Fishery
HGb 1
8
NA
NA
42
13,479
452
OFL
74
61
13
82
18,696
541
ABC
67
56
11
74
15,574
494
10
NA
NA
48
15,574
494
344
329
329
312
298
298
2,194
2,097
2,097
154
147
147
337
1,517
2,652
800
91,102
11,052
5,110
1,143
2,499
313
1,450
2,536
765
87,094
10,090
4,885
1,093
2,389
4,112
3,425
3,200
2,221
313
1,450
2,536
765
50,000
10,090
4,871
1,039
2,000
2,603
822
1,600
y/
4,753
3,042
y/
4,340
2,908
y/
4,340
2,908
8,489
7,750
6,950
5,789
3,089
2,573
E:\FR\FM\19SEP2.SGM
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5,606
1,990
500
1,683
890
328
280
2,051
147
311
1,383
2,451
731
48,404
9,874
4,593
1,028
1,852
2,553
821
1,094
y/
4,318
2,587
See
Table 1c
1,986
483
1,618
889
EP19SE18.001
Stocks/Stock Complexes
COWCODc/
COW COD
COW COD
YELLOWEYE ROCKFISH d/
Arrowtooth Flounder e/
Big Skate f/
ACLa1
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Spiny Dogfish eel
Splitnose Rockfish ff/
Starry Flounder gg/
Widow Rockfish hh/
Yellowtail Rockfish ii/
Black Rockfish/Blue
Rockfish/Deacon Rockfish jj/
Coastwide
S. of 40°10' N. lat.
Coastwide
Coastwide
N. of 40°10' N. lat.
Oregon (Between 46° 16'
N. lat. and 42° N. lat.)
Oregon (Between 46° 16'
N. lat. and 42° N. lat.)
Washington (N. of 46° 16'
N. lat.)
N. of 40°1 0' N. lat.
N. of 40°1 0' N. lat.
N. of 40°10' N. lat.
S. of 40°10' N. lat.
S. of 40°10' N. lat.
S. of 40°10' N. lat.
Cabezon/Kelp Greenling kk/
Cabezon/Kelp Greenling ll/
Nearshore Rockfish mm/
Shelf Rockfish nn/
Slope Rockfish oo/
Nearshore Rockfish pp/
Shelf Rockfish qq/
Slope Rockfish rr/
Other Flatfish ss/
Other Fish ttl
Coastwide
Coastwide
2,486
1,831
652
12,375
6,568
2,071
1,750
452
11,831
5,997
2,071
1,750
452
11,831
5,997
677
617
617
230
218
218
13
11
11
91
2,309
1,887
1,300
1,919
856
8,750
286
81
2,054
1,746
1,145
1,625
744
6,498
239
81
2,054
1,746
1,142
1,625
744
6,498
239
1,738
1,733
433
11,583
4,952
616
218
11
79
1,977
1,665
1,138
1,546
724
6,249
230
a/ Annual catch limits (ACLs), annual catch targets (ACTs) and harvest guidelines (HGs) are
specified as total catch values.
b/ Fishery HGs means the HG or quota after subtracting Pacific Coast treaty Indian tribes
allocations and projected catch, projected research catch, deductions for fishing mortality in nongroundfish fisheries, and deductions for EFPs from the ACL or ACT.
c/ Cowcod south of 40°10' N lat. 2 mt is deducted from the ACL to EFP fishing (less than 0.1
mt) and research activity (2 mt), resulting in a fishery HG of 8 mt. Any additional mortality in
research activities will be deducted from the ACL. A single ACT of 6 mt is being set for the
Conception and Monterey areas combined.
d/ Y elloweye rockfish. The 48 mt ACL is based on the current rebuilding plan with a target year
accommodate the Tribal fishery (2.3 mt), the incidental open access fishery (0.62 mt), EFP catch
(0.24 mt) and research catch (2.92 mt), resulting in a fishery HG of 42 mt. The non-trawl HG is
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47445
38.6 mt. The non-nearshore HG is 2.0 mt and the nearshore HG is 6.0 mt. Recreational HGs are:
10 mt (Washington); 8.9 mt (Oregon); and 11.6 mt (California). In addition, there are the
following ACTs: non-nearshore (1.6 mt), nearshore (4.7 mt), Washington recreational (7.8 mt),
Oregon recreational (7.0 mt), and California recreational (9.1 mt).
e/ Arrowtooth flounder. 2,094.9 mt is deducted from the ACL to accommodate the Tribal fishery
(2,041 mt), the incidental open access fishery (40.8 mt), EFP fishing (0.1 mt), and research catch
(13 mt), resulting in a fishery HG of 13,479 mt.
f/ Big skate. 41.9 mt is deducted from the ACL to accommodate the Tribal fishery (15 mt), the
incidental open access fishery (21.3 mt), EFP fishing (0.1 mt), and research catch (5.5 mt),
resulting in a fishery HG of 452 mt.
g/ Black rockfish (California). 1.3 mt is deducted from the ACL to accommodate EFP fishing
(1.0 mt) and incidental open access fishery (0.3 mt), resulting in a fishery HG of 328 mt.
h/ Black rockfish (Washington). 18.1 mt is deducted from the ACL to accommodate the Tribal
fishery (18 mt) and research catch (0.1 mt), resulting in a fishery HG of280 mt.
i/ Bocaccio south of 40°10' N lat. The stock is managed with stock-specific harvest
specifications south of 40°10' N. lat. and within the Minor Shelf Rockfish complex north of
40°10' N.lat. 46.1 mt is deducted from the ACL to accommodate the incidental open access
fishery (0.5 mt), EFP catch (40 mt) and research catch (5.6 mt), resulting in a fishery HG of
2, 051 mt. The California recreational fishery south of 40°1 0' N lat has an HG of 863.4 mt.
j/ Cabezon (California). 0.3 mt is deducted from the ACL to accommodate the incidental open
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k/ California scorpionfish south of 34 °27' N lat. 2.4 mt is deducted from the ACL to
accommodate the incidental open access fishery (2.2 mt) and research catch (0.2 mt), resulting in
a fishery HG of 311 mt.
11 Canary rockfish. 67.1 mt is deducted from the ACL to accommodate the Tribal fishery (50 mt),
the incidental open access fishery (1.3 mt), EFP catch (8 mt), and research catch (7.8 mt),
resulting in a fishery HG of 1,383 mt. Recreational HGs are: 47.1 mt (Washington); 70.7 mt
(Oregon); and 127.3 mt (California).
m/ Chilipepper rockfish south of 40°10' N lat. Chilipepper are managed with stock-specific
harvest specifications south of 40°10'N. lat. and within the Minor Shelf Rockfish complex north
of 40°10' N. lat. 84.9 mt is deducted from the ACL to accommodate the incidental open access
fishery (11.5 mt), EFP fishing (60 mt), and research catch (13.4 mt), resulting in a fishery HG of
2,451 mt.
n/ Darkblotched rockfish. 33.8 mt is deducted from the ACL to accommodate the Tribal fishery
(0.2 mt), the incidental open access fishery (24.5 mt), EFP catch (0.6 mt), and research catch (8.5
mt) resulting in a fishery HG of 731 mt.
o/ Dover sole. 1,595.6 mt is deducted from the ACL to accommodate the Tribal fishery (1,497
mt), the incidental open access fishery (49.3 mt), EFP fishing (0.1 mt), and research catch (49.2
mt), resulting in a fishery HG of 48,404 mt.
p/ English sole. 216.2 mt is deducted from the ACL to accommodate the Tribal fishery (200 mt),
the incidental open access fishery (8.1 mt), EFP fishing (0.1 mt), and research catch (8 mt),
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47447
q/ Lingcod north of 40°10' N lat. 278 mt is deducted from the ACL for the Tribal fishery (250
mt), the incidental open access fishery (9.8 mt), EFP catch (1.6 mt) and research catch (16.6 mt),
resulting in a fishery HG of 4,593 mt.
r/ Lingcod south of 40°1 0' N lat. 11.3 mt is deducted from the ACL to accommodate the
incidental open access fishery (8.1 mt) and research catch (3 .2 mt), resulting in a fishery HG of
1,028 mt.
s/ Longnose skate. 148.3 mt is deducted from the ACL to accommodate the Tribal fishery (130
mt), incidental open access fishery (5.7 mt), EFP catch (0.1 mt), and research catch (12.5 mt),
resulting in a fishery HG of 1,852 mt.
tl Longspine thorny head north of 34°27' N. lat. 50.4 mt is deducted from the ACL to
accommodate the Tribal fishery (30 mt), the incidental open access fishery (6.2 mt), and research
catch (14.2 mt), resulting in a fishery HG of2,553 mt.
u/ Longspine thorny head south of 34 °27' N. lat. 1.4 mt is deducted from the ACL to
accommodate research catch, resulting in a fishery HG of 821 mt.
v/ Pacific cod. 506.2 mt is deducted from the ACL to accommodate the Tribal fishery (500 mt),
research catch (5.5 mt), EFP fishing (0.1 mt), and the incidental open access fishery (0.6 mt),
resulting in a fishery HG of 1,094 mt.
w/ Pacific whiting. Pacific whiting are assessed annually. The final specifications will be
determined consistent with the U.S.-Canada Pacific Whiting Agreement and will be announced
after the Council's April2019 meeting.
x/ Pacific ocean perch north of 40°10' N lat. 22.4 mt is deducted from the ACL to accommodate
research catch (3 .1 mt) resulting in a fishery HG of 4,318 mt.
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the Tribal fishery (9.2 mt), the incidental open access fishery (10 mt), EFP fishing (0.1 mt), and
47448
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
y/ Petrale sole. 320.6 mt is deducted from the ACL to accommodate the Tribal fishery (290 mt),
the incidental open access fishery (6.4 mt), EFP catch (0.1 mt), and research catch (24.1 mt),
resulting in a fishery HG of 2,587 mt.
z/ Sablefish north of36° N lat. The 40-10 adjustment is applied to the ABC to derive a coastwide
ACL value because the stock is in the precautionary zone. This coastwide ACL value is not
specified in regulations. The coastwide ACL value is apportioned north and south of 36° N. lat.,
using the 2003-2014 average estimated swept area biomass from the NMFS NWFSC trawl
survey, with 73.8 percent apportioned north of36° N. lat. and 26.2 percent apportioned south of
36° N. lat. The northern ACL is 5,606 mt and is reduced by 561 mt for the Tribal allocation (10
percent of the ACL north of36° N. lat.). The 561 mt Tribal allocation is reduced by 1.5 percent
to account for discard mortality. Detailed sablefish allocations are shown in Table 1c.
aa/ Sablefish south of 36° N lat. The ACL for the area south of 36° N. lat. is 1,990 mt (26.2
percent of the calculated coastwide ACL value). 4.2 mt is deducted from the ACL to
accommodate the incidental open access fishery (1.8 mt) and research catch (2.4 mt), resulting in
a fishery HG of 1,986 mt.
bb/ Shortbelly rockfish. 17.2 mt is deducted from the ACL to accommodate the incidental open
access fishery (8.9 mt), EFP catch (0.1 mt), and research catch (8.2 mt), resulting in a fishery HG
of 483 mt.
eel Shorts pine thorny head north of 34 °27' N. lat. 65.3 mt is deducted from the ACL to
accommodate the Tribal fishery (50 mt), the incidental open access fishery (4.7 mt), EFP catch
(0.1 mt), and research catch (10.5 mt), resulting in a fishery HG of 1,618 mt for the area north of
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34°27' N. lat.
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47449
dd/ Shortspine thomyhead south of34°27' N. lat. 1.2 mt is deducted from the ACL to
accommodate the incidental open access fishery (0.5 mt) and research catch (0.7 mt), resulting in
a fishery HG of 889 mt for the area south of 34 °27' N. lat.
eel Spiny dogfish. 333 mt is deducted from the ACL to accommodate the Tribal fishery (275 mt),
the incidental open access fishery (22.6 mt), EFP catch (1.1 mt), and research catch (34.3 mt),
resulting in a fishery HG of 1,738 mt.
ff/ Splitnose rockfish south of 40°10' N lat. Splitnose rockfish in the north is managed in the
Slope Rockfish complex and with stock-specific harvest specifications south of 40°10' N. lat.
16.6 mt is deducted from the ACL to accommodate the incidental open access fishery (5.8 mt),
research catch (9.3 mt) and EFP catch (1.5 mt), resulting in a fishery HG of 1,733 mt.
gg/ Starry flounder. 18.8 mt is deducted from the ACL to accommodate the Tribal fishery (2 mt),
EFP catch (0.1 mt), research catch (0.6 mt), and the incidental open access fishery (16.1 mt),
resulting in a fishery HG of 433 mt.
hh/ Widow rockfish248.4 mt is deducted from the ACL to accommodate the Tribal fishery (200
mt), the incidental open access fishery (3.1 mt), EFP catch (28 mt) and research catch (17.3 mt),
resulting in a fishery HG of 11,583 mt.
ii/ Yellowtail rockfish north of 40°10' N lat. 1,045.1 mt is deducted from the ACL to
accommodate the Tribal fishery (1,000 mt), the incidental open access fishery (4.5 mt), EFP
catch (20 mt) and research catch (20.6 mt), resulting in a fishery HG of 4,952 mt.
jj/ Black rockfish/Blue rockfish/Deacon rockfish (Oregon). 1.2 mt is deducted from the ACL to
accommodate the incidental open access fishery (0.3 mt) and EFP catch (0.9 mt), resulting in a
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fishery HG of 616 mt.
47450
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kk/ Cabezon/kelp greenling (Oregon). 0.2 mt is deducted from the ACL to accommodate EFP
catch, resulting in a fishery HG of 218 mt.
11/ Cabezon/kelp greenling (Washington). There are no deductions from the ACL so the fishery
HG is equal to the ACL of 11 mt.
mm/Nearshore Rockfish north of 40°10' N lat. 2.8 mt is deducted from the ACL to
accommodate the Tribal fishery (1.5 mt), EFP fishing (0.1 mt), research catch (0.3 mt) and the
incidental open access fishery (0.9 mt), resulting in a fishery HG of 79 mt.
nn/ Shelf Rockfish north of 40°10' N lat. 76.9 mt is deducted from the ACL to accommodate the
Tribal fishery (30 mt), the incidental open access fishery (17.7 mt), EFP catch (4.5 mt), and
research catch (24.7 mt), resulting in a fishery HG of 1,977 mt.
oo/ Slope Rockfish north of 40°10' N lat. 80.8 mt is deducted from the ACL to accommodate the
Tribal fishery (36 mt), the incidental open access fishery (21.7 mt), EFP catch (1.5 mt), and
research catch (21.6 mt), resulting in a fishery HG of 1,665 mt.
pp/ Nearshore Rockfish south of 40°10' N lat. 4.1 mt is deducted from the ACL to accommodate
the incidental open access fishery (1.4 mt) and research catch (2.7 mt), resulting in a fishery HG
of 1,138 mt.
qq/ Shelf Rockfish south of 40°10' N lat. 79.1 mt is deducted from the ACL to accommodate the
incidental open access fishery (4.6 mt), EFP catch (60 mt), and research catch (14.5 mt),
resulting in a fishery HG of 1,546 mt.
rr/ Slope Rockfish south of 40°10' N lat. 20.2 mt is deducted from the ACL to accommodate the
incidental open access fishery (16.9 mt), EFP catch (1 mt), and research catch (2.3 mt), resulting
fishery south of 40°1 0' N lat. set equal to the species' contribution to the 40-1 0-adjusted ACL.
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in a fishery HG of 724 mt. Blackgill rockfish has a stock-specific HG for the entire groundfish
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
47451
Harvest ofblackgill rockfish in all groundfish fisheries south of 40°10' N lat. counts against this
HG of 159 mt.
ss/ Other Flatfish. The Other Flatfish complex is comprised of flatfish species managed in the
PCGFMP that are not managed with stock-specific OFLs/ABCs/ACLs. Most of the species in
the Other Flatfish complex are unassessed and include: butter sole, curlfin sole, flathead sole,
Pacific sanddab, rock sole, sand sole, and rex sole. 249.5 mt is deducted from the ACL to
accommodate the Tribal fishery (60 mt), the incidental open access fishery (161.6 mt), EFP
fishing (0.1 mt), and research catch (27.8 mt), resulting in a fishery HG of 6,249 mt.
ttl Other Fish. The Other Fish complex is comprised of kelp greenling off California and leopard
shark coastwide. 8.9 mt is deducted from the ACL to accommodate the incidental open access
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fishery (8.8 mt) and research catch (0.1 mt), resulting in a fishery HG of 230 mt.
47452
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
Table lb. to Part 660, Subpart C-2019, Allocations by Species or Species Group (Weight
in Metric Tons)
Area
Fishery HG
or ACT a/b/
%
Trawl
Mt
Non-Trawl
%
Mt
Arrowtooth flounder
Coastwide
13,479.1
95%
12,805.1
5%
674.0
Big skate a/
Coastwide
452.1
95%
429.5
5%
22.6
Bocaccio a/
S of 40°10' N. lat.
2,050.9
39%
800.7
61%
1,250.2
Canary rockfish a/c/
Coastwide
1,382.9
72%
999.6
28%
383.3
Chili pepper rockfish
S of 40°10' N. lat.
2,451.1
75%
1,838.3
25%
612.8
COWCOD a/b/
S of 40°10' N. lat.
6.0
36%
2.2
64%
3.8
Darkblotched rockfish d/
Coastwide
731.2
95%
694.6
5%
36.6
Dover sole
Coastwide
48,404.4
95%
45,984.2
English sole
Coastwide
9,873.8
95%
9,380.1
Lingcod
N of 40' 10° N. lat.
4,593.0
45%
2,066.9
Lingcod
S of 40' 10° N. lat.
1,027.7
45%
462.5
55%
565.2
Longnose skate a/
Coastwide
1,851.7
90%
1,666.5
10%
185.2
Longspine thornyhead
N of 34°27' N. lat.
2,552.6
95%
2,425.0
5%
127.6
Pacific cod
Coastwide
1,093.8
95%
1,039.1
5%
54.7
Pacific whiting
Coastwide
TBD
100%
TBD
0%
TBD
Pacific ocean perch e/
N of 40°10' N. lat.
4,317.6
95%
4,101.7
5%
215.9
Petrale sole
Coastwide
2,587.4
95%
2,458.0
5%
129.4
Sablefish
N of36°N.lat.
NA
Sablefish
S of 36° N. lat.
1,985.8
42%
834.0
58%
1,151.8
Shortspine thornyhead
N of 34°27' N. lat.
1,617.7
95%
1,536.8
5%
80.9
Shortspine thornyhead
Splitnose rockfish
S of 34°27' N. lat.
S of 40°10' N. lat.
888.8
NA
95%
50.0
1,646.7
NA
5%
838.8
86.7
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5% 2,420.2
5%
493.7
55% 2,526.2
See Table 1c
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Stocks/Stock Complexes
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47453
1,733.4
Starry flounder
Coastwide
433.2
50%
216.6
50%
216.6
Widow rockfish f/
Coastwide
11,582.6
91%
10,540.2
9%
1,042.4
YELLOWEYE ROCKFISH
Coastwide
41.9
8%
3.4
92%
38.6
Yellowtail rockfish
Minor Shelf Rockfish North
a/
Minor ShelfRockfish South
a/
N of 40°10' N. lat.
4,951.9
88%
4,357.7
12%
594.2
N of 40°10' N. lat.
1,977.1
60.2%
1,190.2 39.8%
786.9
S of 40°10' N. lat.
1,545.9
12.2%
188.6 87.8%
1,357.3
Minor Slope Rockfish North
N of 40°1 0' N. lat.
1,665.2
81%
1,348.8
19%
316.4
Minor Slope Rockfish South
S of 40°1 0' N. lat.
723.8
63%
456.0
37%
267.8
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Other Flatfish
Coastwide
6,248.5
90%
5,623.7
10%
624.9
a/ Allocations decided through the biennial specification process.
b/ The cowcod fishery harvest guideline is further reduced to an ACT of 6.0 mt.
c/ 46 mt of the total trawl allocation of canary rockfish is allocated to the MS and C/P sectors, as follows:
30 mt for the MS sector, and 16 mt for the C/P sector.
d/ Consistent with regulations at §660.55(c), 9 percent (62.5 mt) of the total trawl allocation for
darkblotched rockfish is allocated to the Pacific whiting fishery, as follows: 26.3 mt for the Shorebased IFQ
Program, 15.0 mt for the MS sector, and 21.3 mt for the C/P sector. The tonnage calculated here for the
Pacific whiting IFQ fishery contributes to the total shorebased trawl allocation, which is found at
§660.140( d)(1 )(ii)(D).
e/ Consistent with regulations at §660.55(c), 17 percent (697.3 mt) of the total trawl allocation for Pacific
ocean perch is allocated to the Pacific whiting fishery, as follows: 292.9 mt for the Shorebased IFQ
Program, 167.4 mt for the MS sector, and 237.1 mt for the C/P sector. The tonnage calculated here for the
Pacific whiting IFQ fishery contributes to the total shorebased trawl allocation, which is found at
§660.140( d)(1 )(ii)(D).
f/ Consistent with regulations at §660.55(c), 10 percent (1,054 mt) of the total trawl allocation for widow
rockfish is allocated to the whiting fisheries, as follows: 442.7 mt for the shorebased IFQ fishery, 253 mt
for the mothership fishery, and 358.4 mt for the catcher/processor fishery. The tonnage calculated here for
the whiting portion of the shorebased IFQ fishery contributes to the total shorebased trawl allocation, which
is found at §660.140(d)(1)(ii)(D).
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Limited Entry
HG
Set-asides
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Year
2019
ACL
5,606
Tribal a/
561
Research
30.68
Recreational
Estimate
6
EFP
1.1
Commercial
HG
5,007
Open Access
HG
mt
Percent
mt
Percent b/
90.6
4,537
9.4
471
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Limited Entry Trawl c/
Limited Entry Fixed Gear d/
Primary
All Trawl
At-sea Whiting
Shorebased IFQ
AllFG
DTL
Year LEAll
2019
4,537
2,631
50
2,581
1,905
1,620
286
a/ The tribal allocation is further reduced by 1.5 percent for discard mortality resulting in 553 mt in 2019.
b/ The open access HG is taken by the incidental OA fishery and the directed OA fishery.
c/ The trawl allocation is 58 percent of the limited entry HG.
d/ The limited entry fixed gear allocation is 42 percent of the limited entry HG.
19SEP2
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Table lc. to Part 660, Subpart C- Sablefish North of 36° N. lat. Allocations, 2019
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
47455
Ta bl e ld . t0 P ar t 660 Su b,part C - At- Sea Wh.f
1 mg F.1s h ery A nnuaIS et -A s1.d es, 2019
'
Stock or Stock Complex
COW COD
YELLOWEYE ROCKFISH
Arrowtooth flounder
Bocaccio
Canary rockfish a/
Chilipepper rockfish
Darkblotched rockfish b/
Dover sole
English sole
Lingcod
Lingcod
Longnose skate
Longspine thornyhead
Longspine thornyhead
Minor Nearshore Rockfish
Minor Nearshore Rockfish
Minor Shelf Rockfish
Minor Shelf Rockfish
Minor Slope Rockfish
Minor Slope Rockfish
Other Fish
Other Flatfish
Pacific cod
Pacific Halibut c/
Pacific ocean perch d/
Pacific Whiting
Petrale sole
Sablefish
Sablefish
Shortspine thornyhead
Shortspine thornyhead
Starry flounder
Widow Rockfish a/
Yellowtail rockfish
Set Aside
(mt)
NA
0
70
NA
Allocation
NA
36.3
5
5
15
NA
5
5
NA
NA
NA
35
NA
100
NA
NA
20
5
10
404.5
Allocation
5
50
NA
30
NA
5
Allocation
300
Area
S. of 40°10 N. lat.
Coastwide
Coastwide
S. of 40°10 N. lat.
Coastwide
S. of 40°10 N. lat.
Coastwide
Coastwide
Coastwide
N. of 40°10 N. lat.
S. of 40°10 N. lat.
Coastwide
N. of34°27 N. lat.
S. of 34°27 N. lat.
N. of 40°10 N. lat.
S. of 40°10 N. lat.
N. of 40°10 N. lat.
S. of 40°10 N. lat.
N. of 40°10 N. lat.
S. of 40°10 N. lat.
Coastwide
Coastwide
Coastwide
Coastwide
N. of 40°10 N. lat.
Coastwide
Coastwide
N. of36° N. lat.
S. of 36° N. lat.
N. of34°27 N. lat.
S. of34°27 N. lat.
Coastwide
Coastwide
N. of 40°10 N. lat.
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a/ See Table 1.b., to Subpart C, for the at-sea whiting allocations for these species.
47456
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*
*
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Table 2a. to Part 660, Subpart C—2020, and
Beyond, Specifications of OFL, ABC,
ACL, ACT and Fishery Harvest
Guidelines (Weights in Metric Tons)
Table 2b. to Part 660, Subpart C—2020, and
Beyond, Allocations by Species or
Species Group [Weight in Metric Tons]
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Table 2c. to Part 660, Subpart C—Sablefish
North of 36° N lat. Allocations, 2020 and
Beyond
Table 2d. to Part 660, Subpart C—At-Sea
Whiting Fishery Annual Set-Asides,
2020 and Beyond
*
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*
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EP19SE18.014
11. Tables 2a to part 660, subpart C
through 2d to part 660, supbart C are
revised to read as follows:
■
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
47457
Table 2a. to Part 660, Subpart C-2020, and Beyond, Specifications of OFL, ABC, ACL,
ACT and Fishery Harvest Guidelines (Weights in Metric Tons)
'
...
StockslStock Co!hplexes ·.· .·•·•
COWCOD c/
COW COD
COW COD
YELLOWEYE ROCKFISH
d/
Arrowtooth Flounder e/
Big Skate f/
Black Rockfish g/
Black Rockfish h/
Bocaccio i/
Cabezonj/
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California Scorpionfish kl
Canary Rockfish 11
Chili pepper Rockfish m/
Darkblotched Rockfish n/
Dover Sole o/
English Sole p/
Lingcod q/
Lingcod r/
Longnose Skate s/
Longspine Thornyhead t/
Longspine Thornyhead u/
Pacific Cod v/
Pacific Whiting w/
Pacific Ocean Perch x/
Petrale Soley/
;
,'
'
·····,•··· .....·••. •··••···
•r '
68
57
11
10
NA
NA
8
NA
NA
84
15,306
541
77
12,750
494
49
12,750
494
43
10,655
452
341
326
326
325
311
2,104
297
2,011
297
2,011
279
1,965
153
331
1,431
2,521
853
92,048
11,101
4,768
977
2,474
146
307
1,368
2,410
815
87,998
10,135
4,558
934
2,365
3,901
3,250
3,200
y/
4,632
2,976
2,221
y/
4,229
2,845
146
307
1,368
2,410
815
50,000
10,135
4,541
869
2,000
2,470
780
1,600
y/
4,229
2,845
8,648
7,896
Coastwide
N. of 34 °27' N. lat.
S. of34°27' N. lat.
6,950
5,789
3,063
2,551
Coastwide
2,472
2,059
146
305
1,301
2,325
781
48,404
9,919
4,263
858
1,852
2,420
779
1,094
y/
4,207
2,524
See
Table 2c
2,028
483
1,604
882
1,726
Coastwide
Coastwide
Coastwide
California (S. of 42° N.
lat.)
Washington (N. of 46° 16'
N. lat.)
S. of 40°10' N. lat.
California (S. of 42° N.
lat.)
S. of34°27' N. lat.
Coastwide
S. of 40°10' N. lat.
Coastwide
Coastwide
Coastwide
N. of 40°10' N. lat.
S. of 40°10' N. lat.
Coastwide
N. of 34 °27' N. lat.
S. of34°27' N. lat.
Coastwide
Coastwide
N. of 40°10' N lat.
Coastwide
Sablefish aa/
Shortbelly Rocktl.sh bb/
Shortspine Thornyhead cc/
Shortspine Thornyhead dd/
Spiny Dogfish eel
S. of 36° N. lat
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(Conception)
(Monterey)
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2,059
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47458
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
Splitnose Rockfish ff/
Starry Flounder gg/
Widow Rockfish hh/
Yellowtail Rockfish ii/
Black Rockfish/Blue
Rockfish/Deacon Rockfish ii/
Cabezon/Kelp Greenling kk/
Cabezon/Kelp Greenling ll/
Nearshore Rockfish mm/
Shelf Rockfish nn/
Slope Rockfish oo/
Nearshore Rockfish pp/
ShelfRockfish qq/
Slope Rockfish rr/
Other Flatfish ss/
Other Fish ttl
S. of 40°10' N. lat.
Coastwide
Coastwide
N. of 40°10' N. lat.
Oregon (Between 46° 16'
N. lat. and 42° N. lat.)
Oregon (Between 46° 16'
N. lat. and 42° N. lat.)
Washington (N. of 46° 16'
N. lat.)
N. of 40°1 0' N. lat.
N. of 40°1 0' N. lat.
N. of 40°10' N. lat.
S. of 40°10' N. lat.
S. of 40°10' N. lat.
S. of 40°10' N. lat.
Coastwide
Coastwide
1,810
652
11,714
6,261
1,731
452
11,199
5,716
1,731
452
11,199
5,716
1,714
433
10,951
4,671
670
611
611
609
216
204
204
204
12
92
2,302
1,873
1,322
1,919
855
8,202
286
10
82
2,048
1,732
1,165
1,626
743
6,041
239
10
82
2,048
1,732
1,163
1,625
743
6,041
239
10
79
1,971
1,651
1,159
1,546
723
5,792
230
a/ Annual catch limits (ACLs), annual catch targets (ACTs) and harvest guidelines (HGs) are
specified as total catch values.
b/ Fishery HGs means the HG or quota after subtracting Pacific Coast treaty Indian tribes
allocations and projected catch, projected research catch, deductions for fishing mortality in nongroundfish fisheries, and deductions for EFPs from the ACL or ACT.
c/ Cowcod south of 40°10' N lat. 2 mt is deducted from the ACL to accommodate EFP fishing
(less than 0.1 mt) and research activity (2 mt), resulting in a fishery HG of 8 mt. Any additional
mortality in research activities will be deducted from the ACL. A single ACT of 6 mt is being set
for the Conception and Monterey areas combined.
d/ Y elloweye rockfish. The 49 mt ACL is based on the current rebuilding plan with a target year
to rebuild of 2029 and an SPR harvest rate of 65 percent. 6.1 mt is deducted from the ACL to
(0.24 mt) and research catch (2.92 mt), resulting in a fishery HG of 43 mt. The non-trawl HG is
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Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
47459
39.5 mt. The non-nearshore HG is 2.1 mt and the nearshore HG is 6.2 mt. Recreational HGs are:
10.2 mt (Washington); 9.1 mt (Oregon); and 11.9 mt (California). In addition, there are the
following ACTs: non-nearshore (1.7 mt), nearshore (4.9 mt), Washington recreational (8.1 mt),
Oregon recreational (7.2 mt), and California recreational (9.4 mt).
e/ Arrowtooth flounder. 2,094.9 mt is deducted from the ACL to accommodate the Tribal fishery
(2,041 mt), the incidental open access fishery (40.8 mt), EFP fishing (0.1 mt), and research catch
(13 mt), resulting in a fishery HG of 10,655 mt.
f/ Big skate. 41.9 mt is deducted from the ACL to accommodate the Tribal fishery (15 mt), the
incidental open access fishery (21.3 mt), EFP fishing (0.1 mt), and research catch (5.5 mt),
resulting in a fishery HG of 452 mt.
g/ Black rockfish (California). 1.3 mt is deducted from the ACL to accommodate EFP fishing
(1.0 mt) and the incidental open access fishery (0.3 mt), resulting in a fishery HG of 325 mt.
h/ Black rockfish (Washington). 18.1 mt is deducted from the ACL to accommodate the Tribal
fishery (18 mt) and research catch (0.1 mt), resulting in a fishery HG of279 mt.
i/ Bocaccio south of 40°10' N lat. The stock is managed with stock-specific harvest
specifications south of 40°10' N. lat. and within the Minor Shelf Rockfish complex north of
40°10' N.lat. 46.1 mt is deducted from the ACL to accommodate the incidental open access
fishery (0.5 mt), EFP catch (40 mt) and research catch (5.6 mt), resulting in a fishery HG of
1,965 mt. The California recreational fishery has an HG of 827.2 mt.
j/ Cabezon (California). 0.3 mt is deducted from the ACL to accommodate the incidental open
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access fishery, resulting in a fishery HG of 146 mt.
47460
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k/ California scorpionfish south of 34 °27' N lat. 2.4 mt is deducted from the ACL to
accommodate the incidental open access fishery (2.2 mt) and research catch (0.2 mt), resulting in
a fishery HG of 305 mt.
11 Canary rockfish. 67.1 mt is deducted from the ACL to accommodate the Tribal fishery (50
mt), the incidental open access fishery (1.3 mt), EFP catch (8 mt), and research catch (7.8 mt),
resulting in a fishery HG of 1,301 mt. Recreational HGs are: 44.3 mt (Washington); 66.5 mt
(Oregon); and 119.7 mt (California).
m/ Chilipepper rockfish south of 40°10' N lat. Chilipepper are managed with stock-specific
harvest specifications south of 40°10'N. lat. and within the Minor Shelf Rockfish complex north
of 40°10' N. lat. 84.9 mt is deducted from the ACL to accommodate the incidental open access
fishery (11.5 mt), EFP fishing (60 mt), and research catch (13.4 mt), resulting in a fishery HG of
2,325 mt.
n/ Darkblotched rockfish. 33.8 mt is deducted from the ACL to accommodate the Tribal fishery
(0.2 mt), the incidental open access fishery (24.5 mt), EFP catch (0.6 mt), and research catch (8.5
mt) resulting in a fishery HG of 781 mt.
o/ Dover sole. 1,595.6 mt is deducted from the ACL to accommodate the Tribal fishery (1,497
mt), the incidental open access fishery (49.3 mt), EFP fishing (0.1 mt), and research catch (49.2
mt), resulting in a fishery HG of 48,404 mt.
p/ English sole. 216.2 mt is deducted from the ACL to accommodate the Tribal fishery (200 mt),
the incidental open access fishery (8.1 mt), EFP fishing (0.1 mt), and research catch (8 mt),
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q/ Lingcod north of 40°10' N lat. 278 mt is deducted from the ACL for the Tribal fishery (250
mt), the incidental open access fishery (9.8 mt), EFP catch (1.6 mt) and research catch (16.6 mt),
resulting in a fishery HG of 4,263 mt.
r/ Lingcod south of 40°1 0' N lat. 11.3 mt is deducted from the ACL to accommodate the
incidental open access fishery (8.1 mt) and research catch (3 .2 mt), resulting in a fishery HG of
858 mt.
s/ Longnose skate. 148.3 mt is deducted from the ACL to accommodate the Tribal fishery (130
mt), incidental open access fishery (5.7 mt), EFP catch (0.1 mt), and research catch (12.5 mt),
resulting in a fishery HG of 1,852 mt.
tl Longspine thomyhead. 50.4 mt is deducted from the ACL to accommodate the Tribal fishery
(30 mt), the incidental open access fishery (6.2 mt), and research catch (14.2 mt), resulting in a
fishery HG of 2,420 mt.
u/ Longspine thorny head south of 34°27' N. lat. 1.4 mt is deducted from the ACL to research
catch, resulting in a fishery HG of 779 mt.
v/ Pacific cod. 506.2 mt is deducted from the ACL to accommodate the Tribal fishery (500 mt),
EFP catch (0.1 mt), research catch (5.5 mt), and the incidental open access fishery (0.6 mt),
resulting in a fishery HG of 1,094 mt.
w/ Pacific whiting. Pacific whiting are assessed annually. The final specifications will be
determined consistent with the U.S.-Canada Pacific Whiting Agreement and will be announced
after the Council's April 2020 meeting.
x/ Pacific ocean perch north of 40°10' N lat. 22.4 mt is deducted from the ACL to accommodate
research catch (3 .1 mt)-resulting in a fishery HG of 4,207 mt.
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47462
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
y/ Petrale sole. 320.6 mt is deducted from the ACL to accommodate the Tribal fishery (290 mt),
the incidental open access fishery (6.4 mt), EFP catch (0.1 mt), and research catch (24.1 mt),
resulting in a fishery HG of 2,524 mt.
z/ Sablefish north of36° N lat. The 40-10 adjustment is applied to the ABC to derive a coastwide
ACL value because the stock is in the precautionary zone. This coastwide ACL value is not
specified in regulations. The coastwide ACL value is apportioned north and south of 36° N. lat.,
using the 2003-2014 average estimated swept area biomass from the NMFS NWFSC trawl
survey, with 73.8 percent apportioned north of36° N. lat. and 26.2 percent apportioned south of
36° N. lat. The northern ACL is 5, 723 mt and is reduced by 572 mt for the Tribal allocation (1 0
percent of the ACL north of36° N. lat.). The 572 mt Tribal allocation is reduced by 1.5 percent
to account for discard mortality. Detailed sablefish allocations are shown in Table 2c.
aa/ Sablefish south of 36° N lat. The ACL for the area south of 36° N. lat. is 2,032 mt (26.2
percent of the calculated coastwide ACL value). 4.2 mt is deducted from the ACL to
accommodate the incidental open access fishery (1.8 mt) and research catch (2.4 mt), resulting in
a fishery HG of2,028 mt.
bb/ Shortbelly rockfish. 17.2 mt is deducted from the ACL to accommodate the incidental open
access fishery (8.9 mt), EFP catch (0.1 mt), and research catch (8.2 mt), resulting in a fishery HG
of 483 mt.
eel Shorts pine thorny head north of 34 °27' N. lat. 65.3 mt is deducted from the ACL to
accommodate the Tribal fishery (50 mt), the incidental open access fishery (4.7 mt), EFP catch
(0.1 mt), and research catch (10.5 mt), resulting in a fishery HG of 1,604 mt for the area north of
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47463
dd/ Shortspine thomyhead south of34°27' N. lat. 1.2 mt is deducted from the ACL to
accommodate the incidental open access fishery (0.5 mt) and research catch (0.7 mt), resulting in
a fishery HG of 882 mt for the area south of 34 °27' N. lat.
eel Spiny dogfish. 333 mt is deducted from the ACL to accommodate the Tribal fishery (275 mt),
the incidental open access fishery (22.6 mt), EFP catch (1.1 mt), and research catch (34.3 mt),
resulting in a fishery HG of 1,726 mt.
ff/ Splitnose rockfish south of 40°10' N lat. Splitnose rockfish in the north is managed in the
Slope Rockfish complex and with stock-specific harvest specifications south of 40°10' N. lat.
16.6 mt is deducted from the ACL to accommodate the incidental open access fishery (5.8 mt),
research catch (9.3 mt) and EFP catch (1.5 mt), resulting in a fishery HG of 1,714 mt.
gg/ Starry flounder. 18.8 mt is deducted from the ACL to accommodate the Tribal fishery (2 mt),
EFP catch (0.1 mt), research catch (0.6 mt), and the incidental open access fishery (16.1 mt),
resulting in a fishery HG of 433 mt.
hh/ Widow rockfish. 248.4 mt is deducted from the ACL to accommodate the Tribal fishery (200
mt), the incidental open access fishery (3.1 mt), EFP catch (28 mt) and research catch (17.3 mt),
resulting in a fishery HG of 10,951 mt.
ii/ Yellowtail rockfish north of 40°10' N lat. 1,045.1 mt is deducted from the ACL to
accommodate the Tribal fishery (1,000 mt), the incidental open access fishery (4.5 mt), EFP
catch (20 mt) and research catch (20.6 mt), resulting in a fishery HG of 4,671 mt.
jj/ Black rockfish/Blue rockfish/Deacon rockfish (Oregon). 1.2 mt is deducted from the ACL to
accommodate the incidental open access fishery (0.3 mt) and EFP catch (0.9 mt), resulting in a
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fishery HG of 609 mt.
47464
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
kk/ Cabezon/Kelp greenling (Oregon). 0.2 mt is deducted from the ACL to accommodate EFP
catch, resulting in a fishery HG of 204 mt.
11/ Cabezon/Kelp greenling (Washington). There are no deductions from the ACL so the fishery
HG is equal to the ACL of 10 mt.
mm/ Nearshore Rockfish north of 40°10' N lat. 2.8 mt is deducted from the ACL to
accommodate the Tribal fishery (1.5 mt), EFP catch (0.1 mt), research catch (0.3), and the
incidental open access fishery (0.9 mt), resulting in a fishery HG of 79 mt.
nn/ Shelf Rockfish north of 40°10' N lat. 76.9 mt is deducted from the ACL to accommodate the
Tribal fishery (30 mt), the incidental open access fishery (17.7 mt), EFP catch (4.5 mt), and
research catch (24.7 mt), resulting in a fishery HG of 1,971 mt.
oo/ Slope Rockfish north of 40°10' N lat. 80.8 mt is deducted from the ACL to accommodate the
Tribal fishery (36 mt), the incidental open access fishery (21.7 mt), EFP catch (1.5 mt), and
research catch (21.6 mt), resulting in a fishery HG of 1,651 mt.
pp/ Nearshore Rockfish south of 40°10' N lat. 4.1 mt is deducted from the ACL to accommodate
the incidental open access fishery (1.4 mt) and research catch (2.7 mt), resulting in a fishery HG
of 1,159 mt.
qq/ Shelf Rockfish south of 40°10' N lat. 79.1 mt is deducted from the ACL to accommodate the
incidental open access fishery (4.6 mt), EFP catch (60 mt), and research catch (14.5 mt),
resulting in a fishery HG of 1,546 mt.
rr/ Slope Rockfish south of 40°10' N lat. 20.2 mt is deducted from the ACL to accommodate the
incidental open access fishery (16.9 mt), EFP catch (1 mt), and research catch (2.3 mt), resulting
fishery south of 40°1 0' N lat. set equal to the species' contribution to the 40-1 0-adjusted ACL.
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in a fishery HG of 723 mt. Blackgill rockfish has a stock-specific HG for the entire groundfish
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
47465
Harvest ofblackgill rockfish in all groundfish fisheries south of 40°10' N lat counts against this
HG of 159 mt.
ss/ Other Flatfish. The Other Flatfish complex is comprised of flatfish species managed in the
PCGFMP that are not managed with stock-specific OFLs/ABCs/ACLs. Most of the species in
the Other Flatfish complex are unassessed and include: butter sole, curlfin sole, flathead sole,
Pacific sanddab, rock sole, sand sole, and rex sole. 249.5 mt is deducted from the ACL to
accommodate the Tribal fishery (60 mt), the incidental open access fishery (161.6 mt), EFP
fishing (0.1 mt), and research catch (27.8 mt), resulting in a fishery HG of 5, 792 mt.
ttl Other Fish. The Other Fish complex is comprised of kelp greenling off California and leopard
shark coastwide. 8.9 mt is deducted from the ACL to accommodate the incidental open access
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fishery (8.8 mt) and research catch (0.1 mt), resulting in a fishery HG of 230 mt.
47466
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
Table 2b. to Part 660, Subpart C-2020, and Beyond, Allocations by Species or Species
Group [Weight in Metric Tons]
o/o
Mt
Non-trawl
o/o
Mt
Arrowtooth flounder
Coastwide
10,655.1
95%
10,122.3
5%
532.8
Big skate a/
Coastwide
S of 40°10' N.
lat.
452.1
95%
429.5
5%
22.6
1,964.9
39%
767.1
61%
1,197.8
1,300.9
72%
940.3
28%
360.6
2,325.1
75%
1,743.8
25%
581.3
COWCOD a/b/
Coastwide
S of 40°10' N.
lat.
S of 40°10' N.
lat.
6.0
36%
2.2
64%
3.8
Darkblotched rockfish c/
Coastwide
781.2
95%
742.1
5%
39.1
Dover sole
Coastwide
48,404.4
95%
45,984.2
5%
2,420.2
English sole
Coastwide
N of 40'10° N.
lat.
S of 40' 10° N.
lat.
9,918.8
95%
9,422.9
5%
495.9
4,263.0
45%
1,918.4
55%
2,344.7
857.7
45%
386.0
55%
471.7
1,851.7
90%
1,666.5
10%
185.2
2,419.6
95%
2,298.6
5%
121.0
Bocaccio a/
Canary rockfish a/d/
Chili pepper rockfish
Lingcod
Lingcod
Longnose skate a/
Coastwide
N of 34°27' N.
lat.
Longspinethornyhead
1,093.8
TBD
95%
100%
1,039.1
f/
5%
0%
54.7
TBD
Pacific ocean perch e/
Coastwide
Coastwide
N of 40°10' N.
lat.
4,206.6
95%
3,996.3
5%
210.3
Petrale sole
Sablefish
Coastwide
N of 36° N. lat.
2,524.4
NA
95%
5%
2,398.2
See Table 2c
126.2
Sablefish
S of36°N.lat.
N of 34°27' N.
lat.
S of34°27' N.
2,027.8
42%
851.7
58%
1,176.1
1,603.7
95%
NA
1,523.5
50.0
5%
NA
80.2
831.8
Pacific cod
Pacific whiting
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Area
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Shortspine thorny head
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Stocks/Stock Complexes
Fishery
HGor
ACTa/
b/
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
47467
881.8
Splitnose rockfish
lat.
S of 40°10' N.
lat.
1,714.4
95%
1,628.7
5%
85.7
Stary flounder
Coastwide
433.2
50%
216.6
50%
216.6
Widow rockfish f/
Coastwide
10,950.6
91%
9,965.0
9%
985.6
YELLOWEYE ROCKFISH
Coastwide
N of 40°1 0' N.
lat.
N of 40°10' N.
lat.
S of 40°10' N.
lat.
N of 40°1 0' N.
lat.
S of 40°10' N.
lat.
42.9
8%
3.4
92%
39.5
4,670.9
88%
4,110.4
12%
560.5
1,971.1
60.2%
1,186.6
39.8%
784.5
1,545.9
12.2%
188.6
87.8%
1,357.3
1,651.2
81%
1,337.5
19%
313.7
722.8
63%
455.4
37%
267.4
Yellowtail rockfish
Minor Shelf Rockfish North
Minor ShelfRockfish South
Minor Slope Rockfish North
Minor Slope Rockfish South
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Other Flatfish
Coastwide
5,791.5
90%
5,212.4
10%
579.2
a/ Allocations decided through the biennial specification process.
b/ The cowcod fishery harvest guideline is further reduced to an ACT of 6.0 mt.
c/46 mt of the total trawl allocation of canary rockfish is allocated to the MS and C/P sectors, as follows:
30 mt for the MS sector, and 16 mt for the C/P sector.
d/ Consistent with regulations at §660.55(c), 9 percent (66.8 mt) of the total trawl allocation for
darkblotched rockfish is allocated to the Pacific whiting fishery, as follows: 28.1 mt for the Shorebased IFQ
Program, 16.0 mt for the MS sector, and 22.7 mt for the C/P sector. The tonnage calculated here for the
Pacitl.c whiting IFQ tl.shery contributes to the total shorebased trawl allocation, which is found at
§660 .140( d)(1 )(ii)(D).
e/ Consistent with regulations at §660.55(c), 17 percent (679.4 mt) of the total trawl allocation for Pacific
ocean perch is allocated to the Pacific whiting fishery, as follows: 285.3 mt for the Shorebased IFQ
Program, 163.0 mt for the MS sector, and 231.0 mt for the C/P sector. The tonnage calculated here for the
Pacific whiting IFQ fishery contributes to the total shorebased trawl allocation, which is found at
§660.140( d)(1 )(ii)(D).
f/ Consistent with regulations at §660.55(c), 10 percent (996.5 mt) of the total trawl allocation for widow
rockfish is allocated to the whiting fisheries, as follows: 418.5 mt for the shorebased IFQ fishery, 239.2 mt
for the mothership fishery, and 338.8 mt for the catcher/processor fishery. The tonnage calculated here for
the whiting portion of the shorebased IFQ fishery contributes to the total shorebased trawl allocation, which
is found at §660.140(d)(1)(ii)(D).
amozie on DSK3GDR082PROD with PROPOSALS2
47468
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Limited Entry
HG
Set-asides
Fmt 4701
Year
2020
ACL
5,723
Tribal aJ
572
Research
30.68
Recreational
Estimate
6
EFP
1.1
Commercial
HG
5,113
Open Access
HG
mt
Percent
mt
Percent b/
90.6
4,632
9.4
481
Sfmt 4725
E:\FR\FM\19SEP2.SGM
Limited Entry Trawl c/
Limited Entry Fixed Gear d/
Year LEAll
All Trawl
At-sea Whiting
Shorebased IFQ
AllFG
Primary
DTL
2020
4,632
50
2,637
292
2,687
1,946
1,654
a/ The tribal allocation is further reduced by 1.5 percent for discard mortality resulting in 563 mt in 2020.
b/ The open access HG is taken by the incidental OA fishery and the directed OA fishery.
c/ The trawl allocation is 58 percent of the limited entry HG
d/ The limited entry fixed gear allocation is 42 percent of the limited entry HG
19SEP2
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
18:17 Sep 18, 2018
EP19SE18.026
Table 2c. to Part 660, Subpart C- Sablefish North of 36° N. lat. Allocations, 2020 and Beyond
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
47469
a/ See Table 1.b., to Subpart C, for the at-sea whiting allocations for these species.
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amozie on DSK3GDR082PROD with PROPOSALS2
Table 2d. to Part 660, Subpart C - At-Sea Whiting Fishery Annual Set-Asides, 2020
an dB eyon d
Set Aside
Stock or Stock Complex
Area
(mt)
COW COD
S. of 40°10 N. lat.
NA
YELLOWEYE ROCKFISH
Coastwide
0
Arrowtooth flounder
Coastwide
70
Bocaccio
S. of 40°10 N. lat.
NA
Canary rockfish a/
Coastwide
Allocation
Chilipepper rockfish
S. of 40°10 N. lat.
NA
Darkblotched rockfish b/
Coastwide
38.7
Dover sole
Coastwide
5
English sole
Coastwide
5
15
Lingcod
N. of 40°10 N. lat.
Lingcod
S. of 40°10 N. lat.
NA
Longnose skate
Coastwide
5
Longspine thornyhead
N. of34°27 N. lat.
5
S. of 34°27 N. lat.
NA
Longspine thornyhead
Minor Nearshore Rockfish
N. of 40°10 N. lat.
NA
Minor Nearshore Rockfish
S. of 40°10 N. lat.
NA
Minor Shelf Rockfish
N. of 40°10 N. lat.
35
Minor Shelf Rockfish
S. of 40°10 N. lat.
NA
Minor Slope Rockfish
N. of 40°10 N. lat.
100
S. of 40°10 N. lat.
NA
Minor Slope Rockfish
Other Fish
Coastwide
NA
Other Flatfish
Coastwide
20
Pacific cod
Coastwide
5
10
Pacific Halibut c/
Coastwide
Pacific ocean perch d/
N. of 40°10 N. lat.
394
Pacific Whiting
Coastwide
Allocation
Petrale sole
Coastwide
5
50
Sablefish
N. of36° N. lat.
Sablefish
S. of 36° N. lat.
NA
Shortspine thornyhead
N. of34°27 N. lat.
30
S. of34°27 N. lat.
NA
Shortspine thornyhead
Starry flounder
Coastwide
5
Widow Rockfish a/
Coastwide
Allocation
300
Yellowtail rockfish
N. of 40°10 N. lat.
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
12. In § 660.130, add paragraph
(c)(2)(ii), revise paragraphs (d)(1)(ii) and
(e)(6), and add paragraph (e)(8) to read
as follows:
■
§ 660.130 Trawl fishery—management
measures.
*
*
*
*
(c) * * *
(2) * * *
(ii) The use of selective flatfish trawl
gear is required inside the Klamath
River Salmon Conservation Zone
(defined at § 660.131(c)(1)) and the
Columbia River Salmon Conservation
Zone (defined at § 660.131(c)(2)).
*
*
*
*
*
(d) * * *
(1) * * *
(ii) North of 40°10′ N lat. POP,
yellowtail rockfish, Washington
cabezon/kelp greenling complex,
Oregon cabezon/kelp greenling
complex, cabezon off California;
*
*
*
*
*
(e) * * *
(6) Bycatch reduction areas (BRAs).
Vessels using midwater groundfish
trawl gear during the applicable Pacific
amozie on DSK3GDR082PROD with PROPOSALS2
*
whiting primary season may be
prohibited from fishing shoreward of a
boundary line approximating the 75 fm
(137 m), 100 fm (183 m), 150 fm (274
m), or 200 fm (366 m) depth contours.
*
*
*
*
*
(8) Salmon conservation zones.
Fishing with midwater trawl gear and
bottom trawl gear, other than selective
flatfish trawl gear, is prohibited in the
following areas:
(i) Klamath River Salmon
Conservation Zone. The ocean area
surrounding the Klamath River mouth
bounded on the north by 41°38.80′ N
lat. (approximately 6 nm north of the
Klamath River mouth), on the west by
124°23′ W long. (approximately 12 nm
from shore), and on the south by
41°26.80′ N lat. (approximately 6 nm
south of the Klamath River mouth).
(ii) Columbia River Salmon
Conservation Zone. The ocean area
surrounding the Columbia River mouth
bounded by a line extending for 6 nm
due west from North Head along 46°18′
N lat. to 124°13.30′ W long., then
southerly along a line of 167 True to
46°11.10′ N lat. and 124°11′ W long.
(Columbia River Buoy), then northeast
along Red Buoy Line to the tip of the
south jetty.
*
*
*
*
*
■ 13. In § 660.131, remove and reserve
paragraph (c)(3) and add paragraph (i).
The addition reads as follows:
§ 660.131 Pacific whiting fishery
management measures.
*
*
*
*
*
(i) Salmon bycatch. This fishery may
be closed through automatic action at
§ 660.60(d)(1)(v) and (vi).
■ 14. In § 660.140, revise paragraphs
(d)(1)(ii)(D), (e)(4)(i), (g)(1),
(h)(1)(i)(A)(3), and (l)(2) to read as
follows:
§ 660.140
Shorebased IFQ Program.
*
*
*
*
*
(d) * * *
(1) * * *
(ii) * * *
(D) For the trawl fishery, NMFS will
issue QP based on the following
shorebased trawl allocations:
IFQ species
Area
Arrowtooth flounder ......................................................
Bocaccio .......................................................................
Canary rockfish .............................................................
Chilipepper ....................................................................
COWCOD .....................................................................
Darkblotched rockfish ...................................................
Dover sole ....................................................................
English sole ..................................................................
Lingcod .........................................................................
Lingcod .........................................................................
Longspine thornyhead ..................................................
Minor Shelf Rockfish complex ......................................
Minor Shelf Rockfish complex ......................................
Minor Slope Rockfish complex .....................................
Minor Slope Rockfish complex .....................................
Other Flatfish complex .................................................
Pacific cod ....................................................................
Pacific ocean perch ......................................................
Pacific whiting ...............................................................
Petrale sole ...................................................................
Sablefish .......................................................................
Sablefish .......................................................................
Shortspine thornyhead .................................................
Shortspine thornyhead .................................................
Splitnose rockfish .........................................................
Coastwide .....................................................................
South of 40°10′ N lat. ...................................................
Coastwide .....................................................................
South of 40°10′ N lat. ...................................................
South of 40°10′ N lat. ...................................................
Coastwide .....................................................................
Coastwide .....................................................................
Coastwide .....................................................................
North of 40°10′ N lat. ...................................................
South of 40°10′ N lat. ...................................................
North of 34°27′ N lat. ...................................................
North of 40°10′ N lat. ...................................................
South of 40°10′ N lat. ...................................................
North of 40°10′ N lat. ...................................................
South of 40°10′ N lat. ...................................................
Coastwide .....................................................................
Coastwide .....................................................................
North of 40°10′ N lat. ...................................................
Coastwide .....................................................................
Coastwide .....................................................................
North of 36° N lat. ........................................................
South of 36° N lat. ........................................................
North of 34°27′ N lat. ...................................................
South of 34°27′ N lat ....................................................
South of 40°10′ N lat. ...................................................
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19SEP2
2019
Shorebased
trawl allocation
(mt)
2020
Shorebased
trawl allocation
(mt)
12,735.1
800.7
946.9
1,838.3
2.2
658.4
45,979.2
9,375.1
2,051.9
462.5
2,420.0
1,155.2
188.6
1,248.8
1,049.1
5,603.7
1,034.1
3,697.3
TBD
2,453.0
2,581.3
834.0
1,511.8
50.0
1,646.7
10,052.3
767.1
887.8
1,743.8
2.2
703.4
45,979.2
9,417.9
1,903.4
386.0
2,293.6
1,151.6
188.6
1,237.5
455.4
5,192.4
1,034.1
3,602.2
TBD
2,393.2
2,636.8
851.7
1,498.5
50.0
1,628.7
EP19SE18.028
47470
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
47471
2019
Shorebased
trawl allocation
(mt)
2020
Shorebased
trawl allocation
(mt)
211.6
9,928.8
3.4
4,057.7
211.6
9,387.1
3.4
3,810.4
IFQ species
Area
Starry flounder ..............................................................
Widow rockfish .............................................................
YELLOWEYE ROCKFISH ............................................
Yellowtail rockfish .........................................................
Coastwide .....................................................................
Coastwide .....................................................................
Coastwide .....................................................................
North of 40°10′ N lat ....................................................
*
*
*
*
*
(e) * * *
(4) * * *
(i) Vessel limits. For each IFQ species
or species group specified in this
paragraph, vessel accounts may not
have QP or IBQ pounds in excess of the
annual QP vessel limit in any year. The
annual QP vessel limit is calculated as
all QPs transferred in minus all QPs
transferred out of the vessel account.
Species category
Annual QP
vessel
limit
(in percent)
amozie on DSK3GDR082PROD with PROPOSALS2
Arrowtooth flounder ..............
Bocaccio S of 40°10′ N lat ...
Canary rockfish .....................
Chilipepper S of 40°10′ N lat
Cowcod S of 40°10′ N lat .....
Darkblotched rockfish ...........
Dover sole ............................
English sole ..........................
Lingcod:
N of 40°10′ N lat ...............
S of 40°10′ N lat ...............
Longspine thornyhead:
N of 34°27′ N lat ...............
Minor rockfish complex N of
40°10′ N lat:
Shelf species .....................
Slope species ....................
Minor rockfish complex S of
40°10′ N lat:
Shelf species .....................
Slope species ....................
Other Flatfish complex .........
Pacific cod ............................
Pacific halibut (IBQ) N of
40°10′ N lat .......................
Pacific ocean perch N of
40°10′ N lat .......................
Pacific whiting (shoreside) ....
Petrale sole ...........................
Sablefish:
N of 36° N lat (Monterey
north) .............................
S of 36° N lat (Conception
area) ..............................
Shortspine thornyhead:
N of 34°27′ N lat ...............
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18:17 Sep 18, 2018
20
15.4
10
15
17.7
6.8
3.9
7.5
5.3
13.3
9
7.5
7.5
rebuilding plan at § 660.40 retained
during that trip and which documents
Species category
any discrepancy the vessel operator and
observer may have in the weights and
S of 34°27′ N lat ...............
9 number of the overfished species, unless
modified inseason under routine
Splitnose rockfish S of
40°10′ N lat .......................
15 management measures at § 660.60(c)(1).
Starry flounder ......................
20 *
*
*
*
*
Widow rockfish .....................
8.5
(l) * * *
Yelloweye rockfish ................
11.4
(2) AMP QP pass through. The 10
Yellowtail rockfish N of
40°10′ N lat .......................
7.5 percent of non-whiting QS will be
reserved for the AMP, but the resulting
Non-whiting groundfish species ....................................
3.2 AMP QP will be issued to all QS permit
owners in proportion to their non*
*
*
*
*
whiting QS until an alternative use of
(g) * * *
AMP QP is implemented.
(1) General. Shorebased IFQ Program
■ 15. In § 660.150, revise paragraph
vessels may discard IFQ species/species (c)(1)(ii) to read as follows:
groups, and the discard mortality must
be accounted for and deducted from QP § 660.150 Mothership (MS) Coop Program.
in the vessel account. With the
*
*
*
*
*
exception of vessels on Pacific whiting
(c) * * *
IFQ trips engaged in maximized
(1) * * *
retention, prohibited and protected
(ii) Species with set-asides for the MS
species must be discarded at sea; Pacific and C/P Coop Programs, as described in
halibut must be discarded as soon as
Table 1d and Table 2d, subpart C.
practicable and the discard mortality
*
*
*
*
*
must be accounted for and deducted
■ 16. In § 660.160, revise paragraph
from IBQ pounds in the vessel account.
(c)(1)(ii) to read as follows:
Non-IFQ species and non-groundfish
Annual QP
vessel
limit
(in percent)
species may be discarded at sea. The
sorting of catch, the weighing and
discarding of any IBQ and IFQ species,
13.5
and the retention of IFQ species must be
9
15 monitored by the observer.
*
*
*
*
20 *
(h) * * *
14.4
(1) * * *
(i) * * *
6
(A) * * *
15
(3) Is exempt from the requirement to
4.5 maintain observer coverage as specified
in this paragraph while remaining
docked in port when the observer makes
4.5
available to the catch monitor an
15 Observer Program reporting form
documenting the weight and number of
9 any overfished species listed under a
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§ 660.160 Catcher/processor (C/P) Coop
Program.
*
*
*
*
*
(c) * * *
(1) * * *
(ii) Species with set-asides for the MS
and C/P Programs, as described in Table
1d and 2d, subpart C.
*
*
*
*
*
■ 17. Revise Tables 1 (North) and 1
(South) to part 660, subpart D to read as
follows:
Table 1 (North) to Part 660, Subpart
D—Limited Entry Trawl Rockfish
Conservation Areas and Landing
Allowances for non-IFQ Species and
Pacific Whiting North of 40°10′ N Lat.
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Table 1 (South) to Part 660, Subpart
D—Limited Entry Trawl Rockfish
Conservation Areas and Landing
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Allowances for non-IFQ Species and
Pacific Whiting South of 40°10′ N Lat.
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19SEP2
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47472
47473
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
Table 1 (South) to Part 660, Subpart D -- Limited Entry Trawl Rockfish Conservation Areas and Landing Allowances for non-IFQ
Species and Pacific Whiting South of 40.10' N. Lat.
This table describes Rockfish Conservation Areas for vessels using groundfish trawl gear. This table describes incidental landing allowances
for vessels registered to a Federal limited entry trawl permit and using groundfish trawl or groundfish non-trawl gears to harvest individual
fishing quota (IFQ) species.
Other Limits and Requirements Apply-- Read§ 660.10- § 660.399 before using this table
JAN-FEB
Rockfish Conservation Area (RCA)
1
11
MAY-JUN
MAR-APR
07/09/2018
JUL-AUG
SEP-OCT
NOV-DEC
:
100 fm line 11 - 150 fm line
South of 40•10' N. lat.
1121
Small footrope trawl gear is required shoreward of the RCA; all trawl gear (large footrope, selective flatfish trawl, midwater trawl, and small footrope
trawl gear) is permitted seaward of the RCA Large footrope trawl gear and midwater trawl gear are prohibited shoreward of the RCA Vessels
fishing groundfish trawl quota pounds with groundfish non-trawl gears, under gear switching provisions at § 660.140, are subject to the
limited entry groundfish trawl fishery landing allowances in this table, regardless of the type of fishing gear used. Vessels fishing
groundfish trawl quota pounds with groundfish non-trawl gears, under gear switching provisions at§ 660.140, are subject to the limited
entry fixed gear non-trawl RCA, as described in Tables 2 (North) and 2 (South) to Part 660, Subpart E.
See§ 660.60, § 660.130, and§ 660.140 for Additional Gear, Trip Limit, and Conservation Area Requirements and Restrictions. See§§ 660.70
660.74 and§§ 660.76-660.79 for Conservation Area Descriptions and Coordinates (including RCAs, YRCA, CCAs, Farallon Islands, Cordell
Banks, and EFHCAs).
-I
State trip limits and seasons may be more restrictive than federal trip limits, particularly in waters off Oregon and California.
)>
2 Longspine thornyhead
llJ
3
r
m
24,000 lb/ 2 months
South of 34°27' N. lat.
Minor Nearshore Rockfish, California
4 Black rockfish, & Oregon
Black/Blue/Deacon rockfish
300 lb/ month
.....Jio.
5 Whiting
midwatertrawl
Before the primary whiting season: CLOSED. --During the primary season: mid-water trawl
permitted in the RCA See §660.131 for season and trip limit details. -- After the primary whiting
season: CLOSED.
large & small footrope gear
Before the primary whiting season: 20,000 lb/trip. --During the primary season: 10,000 lb/trip. -After the primary whiting season: 10,000 lb/trip.
6
7
50 lb/ month
8 Cabezon
9 Shortbelly rockfish
0
s:::::
,....
-
:::r
Unlimited
10 Spiny dogfish
60,000 lb/ month
5,000 lb/ 2
months
11 Big skate
25,000 lb/ 2
months
30,000 lb/ 2
months
35,000 lb/ 2
months
12 Longnose skate
Unlimited
13 California scorpionfish
Unlimited
14 Other Fish
-en
31
10,000 lb/ 2
months
5,000 lb/ 2
months
Unlimited
1/ The Rockfish Conservation Area is an area closed to fishing by particular gear types, bounded by lines specifically defined by latitude and longitude
coordinates set out at§§ 660.71-660.74. This RCA is not defined by depth contours, and the boundary lines that define the RCA may close areas
that are deeper or shallower than the depth contour. Vessels that are subject to the RCA restrictions may not fish in the RCA, or operate in the
RCA for any purpose other than transiting.
2/ South of 34°27' N. lat., the RCA is 100 fm line- 150 fm line along the mainland coast; shoreline- 150 fm line around islands.
3/ "Other Fish" are defined at§ 660.11 and include kelp greenling off California and leopard shark.
18. In § 660.230, revise paragraphs
(c)(2)(ii) and (d)(10)(ii) and add
paragraph (f) to read as follows:
amozie on DSK3GDR082PROD with PROPOSALS2
■
§ 660.230 Fixed gear fishery—
management measures.
*
*
*
(c) * * *
(2) * * *
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*
*
18:17 Sep 18, 2018
Jkt 244001
(ii) North of 40°10′ N lat.—POP,
yellowtail rockfish, cabezon (California),
Washington cabezon/kelp greenling
complex, Oregon cabezon/kelp
greenling complex;
*
*
*
*
*
(d) * * *
(10) * * *
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(ii) Fishing for rockfish and lingcod is
permitted shoreward of the 40 fm (73 m)
depth contour within the CCAs when
trip limits authorize such fishing, and
provided a valid declaration report as
required at § 660.13(d), subpart C, has
been filed with NMFS OLE.
*
*
*
*
*
E:\FR\FM\19SEP2.SGM
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EP19SE18.030
To convert pounds to kilograms, divide by2.20462, the number of pounds in one kilogram
47474
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
(f) Salmon bycatch. This fishery may
be closed through automatic action at
§ 660.60(d)(1)(v) and (vi).
■ 19. In § 660.231, revise paragraph
(b)(3)(i) to read as follows:
§ 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
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*
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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
limited entry permits is subject to per
vessel limits for species other than
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sablefish, and to per vessel limits when
participating in the daily trip limit
fishery for sablefish under § 660.232. In
2019, the following annual limits are in
effect: Tier 1 at 47,637 lb (21,608 kg),
Tier 2 at 21,653 lb (9,822 kg), and Tier
3 at 12,373 lb (5,612 kg). In 2020 and
beyond, the following annual limits are
in effect: Tier 1 at 48,642 lb (22,064 kg),
Tier 2 at 22,110 lb (10,029 kg), and Tier
3 at 12,634 lb (5,731 kg).
*
*
*
*
*
■ 20. Revise Tables 2 (North) and 2
(South) to part 660, subpart E, to read
as follows:
Table 2 (North) to Part 660, Subpart
E—Non-Trawl Rockfish Conservation
Areas and Trip Limits for Limited Entry
Fixed Gear North of 40°10′ N Lat.
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47475
Table 2 (North) to Part 660, Subpart E -- Non-Trawl Rockfish Conservation Areas and Trip Limits for Limited Entry Fixed Gear
North of 40°1 0' N. lat.
Other limits and requirements apply·· Read §§660 10 through 660.399 before us1ng th1s table
JAN-FEB
MAY-JUN
MAR-APR
07/09/2018
JUL-AUG
SEP-OCT
NOV-DEC
Rockfish Conservation Area (RCA) 11 :
shoreline - 100 fm line 11
1
North of 46·16' 1'-1 lat
2
46.16' N lat - 4iOO' ~J Iat
30fm line -100fm line
3
42'00' N lat - 40'10' ~J lat.
301m line -100fm line
11
11
11
11
See §§660.60 and 660.230 for additional gear, trip lin-it and conservation area requirements and restrictions. See §§660.70-660.74 and
§§660.76-660.79 for conservation area descriptions and coordinates (including RCAs, YRCAs, CCAs, Farallon Islands, Cordell Banks, and
EFHCAs).
State trip limits and seasons may be more restrictive than Federal trip limits or seasons, particularly in 11vaters off Oregon and California
21
4
Minor Slope Rockfish & Darkblotched
rockfish
500 lbl month
1,800 lbl 2 months
5 Pacific ocean perch
6 Sable fish
7 Longspine thornyhead
8
1 200 lblweek, not to exceed 3 600 lb/2 months
10,000 lb/2 months
I
2,000 lbl 2 months
Shortspine thornyhead
2,500 lbl 2 months
9
10
11
12
13
14
15
flounder, Other Flatfish
16
Minor Shelf Rockfish
Widow rockfish
5,000 lbl month
Dover sole, arrowtooth flounder,
petrale sole, English sole, starry
31
South of 42° ~J lat, when fishing for "other flatfish," vessels using hook-and-l1ne gear with no more
than 12 hooks per l1ne, using hooks no larger than "Number 2" hooks, which measure 0.44 in (11
mm) point to shan" and up to two 1 lb (0.45 kg) we1ghts per line, are not subject to the RCAs.
-I
)>
10,000 lbl tnp
llJ
Whiting
21
,
Shortbelly, &
r-
200 lbl month
17 Ye llowtai I rockfish
m
1,000 lblmonth
18 Canary rockfish
300 lb/2 months
19 Yelloweye rockfish
1\)
CLOSED
-z
Minor Nearshore Rockfish, Washington
20 Black rockfish & Oregon
Black/blue/deacon rockfish
North of 42'00'
21
~I
4iOO' N. lat.- 40'10' ~~ lat.
22
5,000 lb/2 months, no more than 1,200 lb of wh1ch may be species other than black rockfish or
Iat
8,500 lbl 2
months no
more than
1,200 lb of
which may be
0
~
blue/deacon rockfish"
r+
-
::::T
7,000 lb/2 months, no more than 1,200 lb of which may be spec1es other than
black rockfish
species other
than black
rockfish
23 Lingcocf;'
~I
24
North of 42'00'
25
42'00' N. lat.- 40,10' ~~ lat.
Iat
2,000 lbl 2 months
1,400 lb/2 months
26 Pacific cod
1,000 lbl 2 months
27 Spiny dogfish
200,000 lb/2 months
1150,0001bl21
months
28 Longnose skate
Unlimited
29 Other Fish 61 & Cabezon in California
Unl1m1ted
30 Oregon Cabezon/Kelp Greenling
Unlimited
31
Big skate
100,000 lbl 2 months
Unl1m1ted
11 The Rockfish Conservation Area is an area closed to fishing by particular gear types, bounded by lines specifically defined by latitude
and longitude coordinates set out at §§ 660 71-660 7 4 This RCA is not defined by depth contours (with the exception of the 20-fm
depth contour boundary south of 42 · N Iat), and the boundary lines that define the RCA may close areas that are deeper or shallower
than the depth contour. Vessels that are subject to RCA restrictions may not fish in the RCA, or operate in the RCA for any purpose
5/The min 1m um size limit for lingcod is 22 inches (56 em) total length r2014
18:17 Sep 18, 2018
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Areas and Trip Limits for Limited Entry
Fixed Gear South of 40°10′ N Lat.
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other than transiting
21 Bocaccio, chilipepper and cowcod are included in the trip limits for Minor Shelf Rockfish and splitnose rockfish is Included 1n the
trip limits for Minor Slope Rockfish.
31 "Other flatfish" are defined at§ 660.11 and include butter sole, curlfin sole, flathead sole Pacific sanddab, rex sole, rock sole, and sand sole.
41 For black rockfish north of Cape Alava (48°09.50' r<. lat.), and between Destruction Is. (47°40' N. lat.) and Leadbetter Pnt. ( 46'38.17' N. lat.),
there is an additional limit of 100 lb or 30 percent by weight of all fish on board, whichever is greater, per vessel, per fishing trip.
47476
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
Table 2 (South) to Part 660, Subpart E -- Non-Trawl RockfiSh Conservation Areas and Trip Limits for Lirmed Entry Fixed Gear
South of 40"10' N. lat.
Other limits and requirements apply
Rockfish Conservation Area (RCA)
1
40.10' N. lat - 34.27' N. lat.
2
South of 34°27' N. lat
07/09/2018
Read §§660 10 through 660 399 before using this table
JAN-FEB
11
MAR-APR
MAY-JUN
JUL-AUG
SEP-OCT
NOV-DEC
:
40 frn line 11 - 125 frn l1ne 11
75 fm line
11
-
150 fm l1ne
11
(also applies around islands)
See §§660.60 and 660.230 tor additional gear, trip limit and conservation area requirements and restrictions. See §§660.70-660.74 and
§§660.76-660. 79 for conservation area descriptions and coordinates (including RCAs, YRCAs, CCAs, Farallon Islands, Cordell Banks, and
EFHCAs).
State trip lim1ts and seasons may be more restricti-.e than Federal trip limits or seasons, particularly in waters off Oregon and Califom1a.
3
Minor Slope rockfish
rockfish
4
Splitnose rockfish
5
6
Sablefish
7
8
9
10
11
12
13
14
15
16
17
18
21
& Darkblotched
40,000 lb/2 months of which no more than
1,3751b may be blackgill rockfish
I
40,000 lb/2 months, of which no more than
1,600 lb may be blackgill rockfish
40,000 lb/2 months
1,200 lb/week, not to exceed 3,600 lb/2 months
40, 10' N lat - 36°00' N lat
2,000 lb/ week
South of 36 °00' N lat
10,000 lb/2 months
Longspine thornyhead
Shortspine thornyhead
flounder, Other Flatfish
31
2,500 lb/2 months
3,000 lb/2 months
Southof34.27' N. lat.
Dover sole, arrowtooth flounder,
petrale sole, English sole, starry
I
2,000 lb/2 months
40.10' N lat. - 34.27' N. lat.
5,000 lb/ month
4i
South of
N. lat., when fishing for "other flatfish," vessels us1ng hook-and-line gear with no more
than 12 hooks per lme, us1ng hooks no larger than "Number 2" hooks, which measure 0.44 1n (11
mm) p:Jint to shank, and up to two 1 lb (0.45 kg) weights per line, are not subject to the RCAs
10,000 lb/ tnp
Whiting
m
19 Minor Shelf Rockfish 21 , Shortbelly rockfish, Widow rockfish (including Chilipepper between 40° 10'- 34°27' N. lat.)
20
40.10' N lat.- 34.27' N. lat.
21
Southof34.27' N. lat.
Minor shelf rockfish, shortbelly, widow rockfish, & chilipepper 2,500 lb/2 months, of which no more
than 500 lb may be any spec1es other than chilipepper
4,000 lb/2
months
CLOSED
-I
:X:.
r-
m
4,000 lb/2 months
N
22 Chilipepper
40, 10' N lat.- 34°27' N. lat. Chilipepper included under min or shelf rockfish, shortbelly and widow rockfish lim its -- See above
23
24
Southof34.27' N. lat.
2,000 lb/2 months this opportunity only available seaward of the non-trawl RCA
26
40.10' N lat.- 34.27' N. lat.
27
Southof34°27' N. lat.
300 lb/2
months
CLOSED
CLOSED
CLOSED
30 Bronze spotted rockfish
31 Bocaccio
CLOSED
33
Southof34.27' N. lat.
-s:::::
300 lb/2 months
29 Cowcod
40, 10' N lat.- 34°27' N. lat.
0
300 lb/2 months
28 Yelloweye rockfish
32
-
CJJ
25 Canary rockfish
::::r
1,000 lb/2 months
1,5001b/2
months
CLOSED
1,500 lb/2 months
34 Minor Nearshore Rockfish, California Black rockfish, & Oregon Black/Blue/Deacon rockfish
35 Shallow nearshore 41
1,2001b/2
months
CLOSED
1,200 lb/2 months
nearshore 51
1,0001b/2
months
CLOSED
1,000 lb/2 months
1,5001b/2
months
CLOSED
36 Deeper
37 California Scorpionfish
200 lb/2
months
38 Lingcod61
CLOSED
39 Pacific cod
1,500 lb/2 months
800 lb/2
months
I
lb~
1600
1300 lb/
month month
1,200 lb/2 months
1,000 lb/2 months
40 Spiny dogfish
200,000 lb/2 months
150,000 lb/2
months
I
41 Long nose skate
42 Other Fish 71 & Cabezon in California
Unl1m1ted
43 Big Skate
Unlimited
100,000 lb/2 months
Unl1m1ted
1/ The Rockfish Conservation Area 1s an area closed to f1sh1ng by particular gear types, bounded by 11nes specifically defined by latitude
and longitude coordinates set out at§§ 660.71-660 7 4. This RCA is not defined by depth contours (with the exception of the 20-fm
depth contour boundary south of 42° N lat ), and the boundary l1nes that define the RCA may close areas that are deeper or shallower
than the depth contour. Vessels that are subject to RCA restrictions may not fish in the RCA, or operate in the RCA for any purp:Jse
other than transiting.
21 POP is included in the trip limits for Minor Slope Rockfish. Blackgill rockfish have a species specific trip sub-limit within the Minor
4/ "Shallow Nearshore" are defined at§ 660.11 under "Groundfish" (7)(i)(B)(1).
51 "Deeper Nearshore" are defined at§ 660.11 under "Groundflsh" (7)(1)(8)(2).
6/The commercial m1mimum size limit for lingcod is 24 inches (61 em) total length South of 42° N lat
7/ "Other Fish" are defined at§ 660 11 and Include kelp greenling off California and leopard shark
.~ .c.2014
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Slope Rockfish cumulative limit Yellowtail rockfish are included in the trip limits for Minor Shelf Rockfish. Bronzespotted rockfish
have a species specific trip limit.
3/ "Other Flatfish" are defmed at§ 660.11 and mclude butter sole, curlfm sole, flathead sole, Pacific sanddab, rex sole, rock sole, and sand sole
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
21. In § 660.330, revise paragraphs
(c)(2)(ii) and (d)(11)(ii) and add
paragraph (f) to read as follows:
■
§ 660.330 Open access fishery—
management measures.
*
*
*
*
(c) * * *
(2) * * *
(ii) North of 40°10′ N lat.—POP,
yellowtail rockfish, cabezon (California),
Washington cabezon/kelp greenling
complex, Oregon cabezon/kelp
greenling complex;
*
*
*
*
*
(d) * * *
(11) * * *
(ii) Fishing for rockfish and lingcod is
permitted shoreward of the 40 fm (73 m)
depth contour within the CCAs when
amozie on DSK3GDR082PROD with PROPOSALS2
*
VerDate Sep<11>2014
18:17 Sep 18, 2018
Jkt 244001
trip limits authorize such fishing, and
provided a valid declaration report as
required at § 660.13(d), has been filed
with NMFS OLE.
*
*
*
*
*
(f) Salmon bycatch. This fishery may
be closed through automatic action at
§ 660.60(d)(1)(v) and (d)(1)(vi).
■ 22. In § 660.333, revise paragraph
(c)(3) to read as follows:
§ 660.333 Open access non-groundfish
trawl fishery—management measures.
*
*
*
*
*
(c) * * *
(3) The landing includes California
halibut of a size required by California
Fish and Game Code section 8392,
which states: ‘‘No California halibut
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47477
may be taken, possessed or sold which
measures less than 22 in (56 cm) in total
length. Total length means the shortest
distance between the tip of the jaw or
snout, whichever extends farthest while
the mouth is closed, and the tip of the
longest lobe of the tail, measured while
the halibut is lying flat in natural
repose, without resort to any force other
than the swinging or fanning of the
tail.’’
*
*
*
*
*
■ 23. Revise Tables 3 (North) and 3
(South) in part 660, subpart F, to read
as follows:
Table 3 (North) to Part 660, Subpart
F—Non-Trawl Rockfish Conservation
Areas and Trip Limits for Open Access
Gears North of 40°10′ N Lat.
E:\FR\FM\19SEP2.SGM
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47478
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
Table 3 (North) to Part 660, Subpart F --Non-Trawl Rockfish Conservation Areas and Trip Limits for Open Access Gears North of
40° 10' N. lat.
Other limits and requirements apply-- Read §§660.10 through 660.399 before using this table
JAN-FEB
Rockfish Conservation Area (RCA)
11
I
IVIAR-APR
I
I
IVIAY-JUN
07/09/2018
JUL-AUG
I
SEP-OCT
I
NOV-DEC
:
shoreline- 100 fm line
1 North of 46° 16' N. lat.
2 46°16' N.lat. -4iOO' N.lat.
3 4ioo· N. lat.- 40° 10' N. lat.
11
11
11
11
11
30fm line -100fm line
30fm line -100fm line
See §§660.60, 660.330 and 660.333 for additional gear, trip limit and conservation area requirements and restrictions. See §§660. 70660.74 and §§660.76.060.79 for conservation area descriptions and coordinates (including RCAs, YRCAs, CCAs, Farallon Islands,
Cordell Bank, and EFHCAs).
State trip limits and seasons may be more restrictive than Federal trip limits or seasons, particularly in Vvaters off Oregon and California.
21
4 Minor Slope Rockfish &
500 pounds/month
Darkblotched rockfish
5 Pacific ocean perch
100 lb/ month
6 Sable fish
300 lb/ day; or one landing per week up to 1,000 lb, not to exceed 2,000 lb/ 2 months
50 lb/ month
50 lb/ month
-I
3,000 lb/ month, no more than 300 lb of which may be species other than Pacific sanddabs.
)>
7 Shortpine thornyheads
8 Longspine thornyheads
9
Dover sole, arrowtooth flounder,
petrale sole, English sole, starry
flounder, Other Flatfish
South of 42° N. lat., when fishing for "Other Flatfish," vessels using hook-and-line gear with no more
than 12 hooks per line, using hooks no larger than "Number 2" hooks, which measure 0.44 in (11
mm) point to shank, and up to two 1 lb (0.45 kg) weights per line are not subject to the RCAs.
31
Whiting
300 lb/ month
21
16
Minor Shelf Rockfish , Shortbelly
rockfish, & Widow rockfish
150 lb/ 2 months
19 Yelloweye rockfish
CLOSED
20 Minor Nearshore Rockfish, Washington Black rockfish, & Oregon Black/Blue/Deacon rockfish
0
21
,....
22
North of 4i 00' N. lat.
5,000 lb/ 2 months, no more than 1,200 lb of which may be species other than black rockfish
8,500 lb/ 2
months, no
more than
1,200 lb of
which may be
species other
than black
rockfish
4ioo· N. lat.- 40°10' N.lat.
7,000 lb/ 2 months, no more than 1,200 lb of which may be species other than
black rockfish
600 lb/ month
1,000 lb/ 2 months
200,000 lb/ 2 months
1
150,000 lb/ 2
months
I
28 Longnose skate
29 Big skate
30 Other Fish 61 & Cabezon in California
Unlimited
31 Oregon Cabezon/Kelp Greenling
Unlimited
18:17 Sep 18, 2018
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-
900 lb/ month
27 Spinydogfish
VerDate Sep<11>2014
..,
::::r
23 LinQcod 51
24
North of 4iOO' N. lat.
25
4iOO' N. lat.- 40°10' N.lat.
26 Pacific cod
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-z
500 lb/ month
18 Canary rockfish
m
w
200 lb/ month
17 Yellowtail rockfish
llJ
r
PO 00000
100,000 lb/ 2 months
Unlimited
Unlimited
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10
11
12
13
14
15
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
VerDate Sep<11>2014
18:17 Sep 18, 2018
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Areas and Trip Limits for Open Access
Gears South of 40°10′ N Lat.
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amozie on DSK3GDR082PROD with PROPOSALS2
Table 3 (South) to Part 660, Subpart
F—Non-Trawl Rockfish Conservation
47479
47480
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
Table 3 (South) to Part 660, Subpart F --Non-Trawl Rockfish Conservation Areas and Trip Limits for Open Access Gears South
of 40°10' N. lat.
Other limits and requirements apply-- Read §§660 10 through 660 399 before using this table
JAN-FEB
IVIAY-JUN I
I IVIAR-APR
Rockfish Conservation Area (RCA)
11
07/09/2018
JUL-AUG
I
SEP-OCT
I
NOV-DEC
:
1 40'10' N. lat.- 34'27' N. lat.
2 South of 34'27' N. lat.
40 fm line
75 fm line
11
-
11
-
125 fm line
11
11
150 fm line (also applies around islands)
See §§660.60 and 660.230 for additional gear, trip limit and conservation area requirements and restrictions. See §§660.70.060.74 and
§§660.76-660.79 for conservation area descriptions and coordinates (including RCAs, YRCAs, CCAs, Farallon Islands, Cordell Banks,
and EFHCAs).
State trip limits and seasons may be more restrictive than Federal trip limits or seasons, particularly in Vvaters off Oregon and California.
21
3
10,000 lb/ 2 months, of which no more than 475110,000 lb/ 2 months, of which no more than 550
lb may be blackgill rockfish
lb may be blackgill rockfish
Minor Slope Rockfish &
Darkblotched rockfish
4 Splitnose rockfish
200 lb/ month
5 Sable fish
6
8
300 lb/ day, or one landing per week of up to 1,600 lb, not to exceed 3,200 lb/ 2 months
South of 36° 00' N. lat.
Shortpine thornyheads and longspine
thornyheads
9
10
11
12
13
14
15
16
17
300 lb/ day or one landing per week up to 1,000 lb, not to exceed 2,000 lb/ 2 months
40°10' N.lat. -36°00' N.lat.
7
CLOSED
-I
50 lb/ day, no more than 1,000 lb/ 2 months
)>
3,000 lb/ month, no more than 300 lb of which may be species other than Pacific sanddabs.
llJ
South of 42° N. lat., when fishing for "other flatfish," vessels using hook-and-line gear w~h no more
than 12 hooks per line, using hooks no larger than "Number 2" hooks, which measure 0.44 in (11
mm) point to shank, and up to two 1 lb (0.45 kg) weights per line are not subject to the RCAs.
m
40° 10' N. lat. - 34° 27' N. lat.
South of 34° 27' N. lat.
Dover sole, arrowtooth flounder,
petrale sole, English sole, starry
flounder, Other Flatfish
31
Whiting
300 lb/ month
w
21
18 Minor Shelf Rockfish , Shortbelly,
Widow rockfish and Chilipepper
19
40°10' N. lat.- 34°27' N.lat.
20
South of 34° 27' N. lat.
21 Canary rockfish
400 lb/ 2
months
1,500 lb/ 2
months
150 lb/2
months
400 lb/ 2 months
CLOSED
1,500 lb/ 2 months
CLOSED
150 lb/ 2 months
22 Yelloweye rockfish
23 Cowcod
24 Bronzespotted rockfish
500 lb/ 2
months
CLOSED
-
CJJ
0
s:::::
,....
-
::::r
CLOSED
CLOSED
CLOSED
25 Bocaccio
r
500 lb/ 2 months
26 Minor Nearshore Rockfish, California Black rockfish, & Oregon Black/Blue/Deacon rockfish
27 Shallow nearshore41
1,200 lb/ 2
months
CLOSED
1,200 lb/ 2 months
28 Deeper nearshore51
1,000 lb/ 2
months
CLOSED
1,000 lb/ 2 months
29 California scorpionfish
1,500 lb/ 2
months
CLOSED
1,500 lb/ 2 months
300 lb/ month
CLOSED
30 Lingcod 61
31 Pacific cod
300 lb/ month
1,000 lb/ 2 months
200,000 lb/ 2 months
150,000 lb/ 2
months
amozie on DSK3GDR082PROD with PROPOSALS2
33 Longnose skate
34 Big skate
35 Other Fish 71 & Cabezon in California
VerDate Sep<11>2014
18:17 Sep 18, 2018
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100,000 lb/ 2 months
Unlimited
Unlimited
Unlimited
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32 Spiny dogfish
BILLING CODE 3510–22–C
24. Amend § 660.360 as follows:
a. Revise paragraphs (c)(1)
introductory text, (c)(1)(i)(D)(1) through
(3), (c)(1)(ii) through (iv), (c)(2)(i)(B),
(c)(3)(i)(A) through (C), (c)(3)(ii)(D),
(c)(3)(iii)(B), (c)(3)(iii)(D), (c)(3)(iv), and
(c)(3)(v)(A) and (B); and
■ b. Add paragraph (d).
The revisions and addition read as
follows:
■
■
§ 660.360 Recreational fishery—
management measures.
amozie on DSK3GDR082PROD with PROPOSALS2
*
*
*
*
*
(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 sublimits for rockfish, lingcod, and cabezon
outlined in paragraph (c)(1)(i)(D) of this
section. In addition to the groundfish
VerDate Sep<11>2014
18:17 Sep 18, 2018
Jkt 244001
bag limit of 9, there will be a flatfish
limit of 3 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) * * *
(D) * * *
(1) West of the Bonilla-Tatoosh line
between the U.S. border with Canada
and the Queets River (Washington state
Marine Area 3 and 4), recreational
fishing for groundfish is prohibited
seaward of a boundary line
approximating the 20 fm (37 m) depth
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47481
contour from June 1 through Labor Day,
except on days when the Pacific halibut
fishery is open in this area it is lawful
to retain lingcod, Pacific cod, and
sablefish seaward of the 20 fm (37 m)
boundary. Yellowtail and widow
rockfish can be retained seaward of 20
fm (37 m) in the months of July and
August on days open to the recreational
salmon fishery. Days open to Pacific
halibut recreational fishing off
Washington and days open to
recreational fishing for salmon are
announced on the NMFS hotline at
(206) 526–6667 or (800) 662–9825.
Coordinates for the boundary line
approximating the 20 fm (37 m) depth
contour are listed in § 660.71, subpart C.
(2) Between the Queets River
(47°31.70′ N lat.) and Leadbetter Point
(46°38.17′ N lat.) (Washington state
Marine Area 2), recreational fishing for
lingcod is prohibited seaward of a
boundary line approximating the 30 fm
(55 m) depth contour from the second
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Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
amozie on DSK3GDR082PROD with PROPOSALS2
47482
Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
Saturday in March through May 31 with
the following exceptions: Recreational
fishing for lingcod is permitted within
the RCA on days that the primary
halibut fishery is open; recreational
fishing for lingcod is allowed on
Sundays in May, but only if the Pacific
halibut recreational fishery in this area
is scheduled to be open for less than
four days. In addition to the RCA
described above, between the Queets
River (47°31.70′ N lat.) and Leadbetter
Point (46°38.17′ N lat.) (Washington
state Marine Area 2), recreational
fishing for lingcod is prohibited January
1 through May 31, June 16 through
August 31, and September 16 through
December 31 seaward of a straight line
connecting all of the following points in
the order stated: 47°31.70′ N lat.,
124°45.00′ W long.; 46°38.17′ N lat.,
124°30.00′ W long. with the following
exceptions: On days that the primary
halibut fishery is open lingcod may be
taken, retained and possessed within
the lingcod area closure; if the Pacific
halibut recreational fishery is scheduled
to be open less than four days, lingcod
may be taken, retained, and possessed
within the lingcod area closure on
Sundays in May. Days open to Pacific
halibut recreational fishing off
Washington are announced on the
NMFS hotline at (206) 526–6667 or
(800) 662–9825. For additional
regulations regarding the Washington
recreational lingcod fishery, see
paragraph (c)(1)(iv) of this section.
Coordinates for the boundary line
approximating the 30 fm (55 m) depth
contour are listed in § 660.71.
(3) Between Leadbetter Point
(46°38.17′ N lat.) and the Columbia
River (46°16.00′ N lat.) (Marine Area 1),
when Pacific halibut are onboard the
vessel, no groundfish may be taken and
retained, possessed or landed, except
sablefish, flatfish species (except
halibut), Pacific cod, and lingcod from
May 1 through September 30. Except
that taking, retaining, possessing or
landing incidental halibut with
groundfish on board is allowed in the
nearshore area on days not open to alldepth Pacific halibut fisheries in the
area shoreward of the boundary line
approximating the 30 fathom (55 m)
depth contour extending from
Leadbetter Point, WA (46°38.17′ N lat.,
124°15.88′ W long.) to the Columbia
River (46°16.00′ N lat., 124°15.88′ W
long.) and from there, connecting to the
boundary line approximating the 40
fathom (73 m) depth contour in Oregon.
Nearshore season days are established
in the annual management measures for
Pacific halibut fisheries, which are
published in the Federal Register and
VerDate Sep<11>2014
18:17 Sep 18, 2018
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are announced on the NMFS halibut
hotline, 1–800–662–9825. Between
Leadbetter Point (46°38.17′ N lat.
124°21.00′ W long.) and 46°33.00′ N lat.
124°21.00′ W long., recreational fishing
for lingcod is prohibited year round
seaward of a straight line connecting all
of the following points in the order
stated: 46°38.17′ N lat., 124°21.00′ W
long.; and 46°33.00′ N lat., 124°21.00′ W
long.
(ii) Rockfish. In areas of the EEZ
seaward of Washington (Washington
Marine Areas 1–4) that are open to
recreational groundfish fishing, there is
a 7 rockfish per day bag limit. Taking
and retaining yelloweye rockfish is
prohibited in all Marine areas.
(iii) Cabezon. In areas of the EEZ
seaward of Washington (Washington
Marine Areas 1–4) that are open to
recreational groundfish fishing, there is
a 1 cabezon per day bag limit.
(iv) Lingcod. In areas of the EEZ
seaward of Washington (Washington
Marine Areas 1–4) that are open to
recreational groundfish fishing and
when the recreational season for lingcod
is open, there is a bag limit of 2 lingcod
per day. The recreational fishing season
for lingcod is open from the second
Saturday in March through the third
Saturday in October.
(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
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
June 1 through August 31, recreational
fishing for groundfish is prohibited
seaward of a recreational RCA boundary
line approximating the 40 fm (73 m)
depth contour, except that fishing for
flatfish (other than Pacific halibut) is
allowed seaward of the 40 fm (73 m)
depth contour when recreational fishing
for groundfish is permitted. Coordinates
for the boundary line approximating the
40 fm (73 m) depth contour are listed at
§ 660.71.
*
*
*
*
*
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Fmt 4701
Sfmt 4702
(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 ‘‘Other Flatfish,’’
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.
(1) Between 42° N lat. (California/
Oregon border) and 40°10′ N lat.
(Northern Management Area),
recreational fishing for all groundfish
(except petrale sole, starry flounder, and
‘‘Other Flatfish’’ as specified in
paragraph (c)(3)(iv) of this section) is
closed from January 1 through April 30;
is prohibited seaward of the 30 fm (55
m) depth contour along the mainland
coast and along islands and offshore
seamounts from May 1 through October
31 (shoreward of 30 fm is open); and is
open at all depths from November 1
through December 31. Coordinates for
the boundary line approximating the 30
fm (55 m) depth contour are listed in
§ 660.71.
(2) Between 40°10′ N lat. and
38°57.50′ N lat. (Mendocino
Management Area), recreational fishing
for all groundfish (except petrale sole,
starry flounder, and ‘‘Other Flatfish’’ as
specified in paragraph (c)(3)(iv) of this
section) is closed from January 1
through April 30; prohibited seaward of
the 20 fm (37 m) depth contour along
the mainland coast and along islands
and offshore seamounts from May 1
through October 31 (shoreward of 20 fm
is open), and is open at all depths from
November 1 through December 31.
(3) Between 38°57.50′ N lat. and
37°11′ N lat. (San Francisco
Management Area), recreational fishing
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Federal Register / Vol. 83, No. 182 / Wednesday, September 19, 2018 / Proposed Rules
for all groundfish (except petrale sole,
starry flounder, and ‘‘Other Flatfish’’ as
specified in paragraph (c)(3)(iv) of this
section) is closed from January 1
through April 1; is prohibited seaward
of the boundary line approximating the
40 fm (73 m) depth contour along the
mainland coast and along islands and
offshore seamounts from April 1
through December 31. Closures around
Cordell Banks (see paragraph (c)(3)(i)(C)
of this section) also apply in this area.
Coordinates for the boundary line
approximating the 40 fm (73 m) depth
contour are listed in § 660.71.
(4) Between 37°11′ N lat. and 34°27′
N lat. (Central Management Area),
recreational fishing for all groundfish
(except petrale sole, starry flounder, and
‘‘Other Flatfish’’ as specified in
paragraph (c)(3)(iv) of this section) is
closed from January 1 through March
31; and is prohibited seaward of a
boundary line approximating the 50 fm
(91 m) depth contour along the
mainland coast and along islands and
offshore seamounts from April 1
through December 31. Coordinates for
the boundary line approximating the 50
fm (91 m) depth contour are specified in
§ 660.72.
(5) South of 34°27′ N lat. (Southern
Management Area), recreational fishing
for all groundfish (except California
scorpionfish, ‘‘Other Flatfish,’’ petrale
sole, and starry flounder) is closed
entirely from January 1 through
February 28. Recreational fishing for all
groundfish (except ‘‘Other Flatfish,’’
petrale sole, and starry flounder, as
specified in paragraph (c)(3)(iv) of this
section) is prohibited seaward of a
boundary line approximating the 75 fm
(137 m) depth contour from March 1
through December 31 along the
mainland coast and along islands and
offshore seamounts, except in the CCAs
where fishing is prohibited seaward of
the 40 fm (73 m) depth contour when
the fishing season is open (see
paragraph (c)(3)(i)(B) of this section).
Coordinates for the boundary lines
approximating the depth contours are
specified at §§ 660.71 through 660.74.
(B) Cowcod conservation areas. The
latitude and longitude coordinates of
the Cowcod Conservation Areas (CCAs)
boundaries are specified at § 660.70. In
general, recreational fishing for all
groundfish is prohibited within the
CCAs, except that fishing for petrale
sole, starry flounder, and ‘‘Other
Flatfish’’ is permitted within the CCAs
as specified in paragraph (c)(3)(iv) of
this section. However, recreational
fishing for the following species is
prohibited seaward of the 40 fm (37 m)
depth contour when the season for those
species is open south of 34°27′ N lat.:
VerDate Sep<11>2014
18:17 Sep 18, 2018
Jkt 244001
Minor Nearshore Rockfish, cabezon,
kelp greenling, lingcod, California
scorpionfish, and shelf rockfish.
Retention of yelloweye rockfish,
bronzespotted rockfish and cowcod is
prohibited within the CCA. [Note:
California state regulations also permit
recreational fishing for California
sheephead, ocean whitefish, and all
greenlings of the genus Hexagrammos
shoreward-of the 40 fm (73 m) depth
contour in the CCAs when the season
for the RCG complex is open south of
34°27′ N lat.] It is unlawful to take and
retain, possess, or land groundfish taken
within the CCAs, except for species
authorized in this section.
(C) Cordell Banks. Recreational
fishing for groundfish is prohibited in
waters less than 100 fm (183 m) around
Cordell Banks as defined by specific
latitude and longitude coordinates at
§ 660.70, subpart C, except that
recreational fishing for petrale sole,
starry flounder, and ‘‘Other Flatfish’’ is
permitted around Cordell Banks as
specified in paragraph (c)(3)(iv) of this
section.
*
*
*
*
*
(ii) * * *
(D) Dressing/filleting. Cabezon, kelp
greenling, and rock greenling taken in
the recreational fishery may not be
filleted at sea. Rockfish skin may not be
removed when filleting or otherwise
dressing rockfish taken in the
recreational fishery.
*
*
*
*
*
(iii) * * *
(B) Bag limits, hook limits. In times
and areas when the recreational season
for lingcod is open, there is a limit of
2 hooks and 1 line when fishing for
lingcod. 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.
(1) The bag limit between 42° N lat.
(California/Oregon border) and 40°10′ N
lat. (Northern Management Area) is 2
lingcod per day.
(2) The bag limit between 40°10′ N lat.
and the U.S. border with Mexico
(Mendocino Management Area, San
Francisco Management Area, Central
Management Area, and Southern
Management Area) is 1 lingcod per day.
*
*
*
*
*
(D) Dressing/filleting. Lingcod filets
may be no smaller than 14 in (36 cm)
in length. Each fillet shall bear an intact
1 in (2.6 cm) square patch of skin.
(iv) ‘‘Other Flatfish,’’ petrale sole, and
starry flounder. Coastwide off
California, recreational fishing for
‘‘Other Flatfish,’’ petrale sole, and starry
flounder, is permitted both shoreward of
PO 00000
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Fmt 4701
Sfmt 9990
47483
and within the closed areas described in
paragraph (c)(3)(i) of this section.
‘‘Other Flatfish’’ are defined at § 660.11,
subpart C, and include butter sole,
curlfin sole, flathead sole, Pacific
sanddab, rex sole, rock sole, and sand
sole. ‘‘Other Flatfish,’’ are subject to the
overall 20-fish bag limit for all species
of finfish, of which there may be no
more than 10 fish of any one species;
there is no daily bag limit for petrale
sole, starry flounder and Pacific
sanddab. There are no size limits for
‘‘Other Flatfish,’’ petrale sole, and starry
flounder. ‘‘Other Flatfish’’, petrale sole,
and starry flounder may be filleted at
sea. Fillets may be of any size, but must
bear intact a one-inch square patch of
skin.
(v) * * *
(A) Seasons. When recreational
fishing for California scorpionfish is
open, it is permitted only outside of the
recreational RCAs described in
paragraph (c)(3)(i) of this section.
(1) Between 40°10′ N lat. and
38°57.50′ N lat. (Mendocino
Management Area), recreational fishing
for California scorpionfish is open from
May 1 through December 31 (i.e., it’s
closed from January 1 through April 30).
(2) Between 38°57.50′ N lat. and
37°11′ N lat. (San Francisco
Management Area), recreational fishing
for California scorpionfish is open from
April 15 through December 31 (i.e., it’s
closed from January 1 through April 14).
(3) Between 37°11′ N lat. and 34°27′
N lat. (Central Management Area),
recreational fishing for California
scorpionfish is open from April 1
through December 31 (i.e., it’s closed
from January 1 through March 31).
(4) South of 34°27′ N lat. (Southern
Management Area), recreational fishing
for California scorpionfish is open from
January 1 through December 31.
(B) Bag limits, hook limits. South of
40°10.00′ N lat., in times and areas
where the recreational season for
California scorpionfish is open there is
a limit of 2 hooks and 1 line, the bag
limit is 5 California scorpionfish per
day. California scorpionfish do not
count against the 10 RCG Complex fish
per day limit. 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.
*
*
*
*
*
(d) Salmon bycatch. Recreational
fisheries that are not accounted for
within pre-season salmon modeling may
be closed through automatic action at
660.60(d)(1)(v) and (d)(1)(vi).
[FR Doc. 2018–19460 Filed 9–18–18; 8:45 am]
BILLING CODE 3510–22–P
E:\FR\FM\19SEP2.SGM
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Agencies
[Federal Register Volume 83, Number 182 (Wednesday, September 19, 2018)]
[Proposed Rules]
[Pages 47416-47483]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-19460]
[[Page 47415]]
Vol. 83
Wednesday,
No. 182
September 19, 2018
Part II
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; 2019-20 Biennial Specifications and
Management Measures; Proposed Rule
Federal Register / Vol. 83 , No. 182 / Wednesday, September 19, 2018
/ Proposed Rules
[[Page 47416]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 660
[Docket No. 180625576-8576-01]
RIN 0648-BH93
Magnuson-Stevens Act Provisions; Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery; 2019-20 Biennial Specifications and
Management Measures
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Proposed rule; request for comments.
-----------------------------------------------------------------------
SUMMARY: This proposed rule would establish the 2019-20 harvest
specifications and management measures 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. This proposed rule would also revise the management measures that
are intended to keep the total catch of each groundfish stock or stock
complex within the harvest specifications. The 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.
DATES: Comments must be received no later than October 19, 2018.
ADDRESSES: Submit your comments, identified by NOAA-NMFS-2018-0056, by
either of the following methods:
Federal e-Rulemaking Portal: Go to www.regulations.gov/#!docketDetail;D=NOAA-NMFS-2018-0056, click the ``Comment Now!'' icon,
complete the required fields, and enter or attach your comments.
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).
FOR FURTHER INFORMATION CONTACT: Keeley Kent, phone: 206-526-4655, fax:
206-526-6736, or email: [email protected].
SUPPLEMENTARY INFORMATION:
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 2018 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.
Executive Summary
Purpose of the Regulatory Action
This proposed rule would implement the 2019-20 harvest
specifications and management measures for groundfish stock taken in
the U.S. exclusive economic zone off the coasts of Washington, Oregon,
and California. The purpose of this proposed rule is to conserve and
manage Pacific Coast groundfish fishery resources to prevent
overfishing, to rebuild overfished stocks, achieve optimum yield (OY),
and ensure that management measures are based on the best scientific
information available. This action proposes harvest specifications for
2019-20 consistent with existing or revised default harvest control
rules for all stocks, and establishes management measures designed to
keep catch within the appropriate limits. The harvest specifications
are set consistent with the OY harvest management framework described
in Chapter 4 of the Pacific Coast Groundfish Fishery Management Plan
(PCGFMP).
Major Provisions
This proposed rule contains two types of major provisions. The
first are the harvest specifications (overfishing limits (OFLs),
acceptable biological catches (ABCs), and annual catch limits (ACLs)),
and the second are management measures designed to keep fishing
mortality within the ACLs. The Council developed the harvest
specifications (OFLs, ABCs, and ACLs) in this rule through a rigorous
scientific review and decision making process, which is described later
in this proposed rule.
The OFL is the maximum sustainable yield (MSY) harvest level and is
an estimate of the catch level above which overfishing is occurring.
The Pacific Fishery Management Council's (Council) Scientific and
Statistical Committee (SSC) recommends OFLs based on the best
scientific information available. The ABC is an annual catch
specification that is the stock or stock complex's OFL reduced by an
estimate of scientific uncertainty. The SSC-recommended method for
incorporating scientific uncertainty is referred to as the P star-sigma
approach, which 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
ACL is a harvest specification set equal to or below the ABC. The
Council recommends ACLs at a level that should achieve OY from the
fishery, which is the amount of fish that will provide the greatest
overall benefit to the Nation, particularly with respect to food
production and recreational opportunities, and taking into account the
protection of marine ecosystems. The ACLs are based on consideration of
conservation objectives, socio-economic concerns, management
uncertainty, and other factors. All known sources of fishing and
scientific research catch are counted against the ACL. Many stocks are
further allocated into harvest guidelines (HGs) or annual catch targets
(ACTs) for the purposes of dividing catch between different gear types
and sectors or building in a precautionary approach to prevent catch
from exceeding an ACL.
This proposed rule includes harvest specifications for the two
overfished stocks managed under the PCGFMP, yelloweye rockfish and
cowcod. For the 2019-20 biennium, NMFS proposes changes to the
yelloweye rockfish rebuilding plan, due to its improved
[[Page 47417]]
stock rebuilding outlook and changes to the needs of fishing
communities, described under section C of this rule. This proposed rule
would modify the harvest control rule for this stock and establish
harvest specifications and management measures consistent with those
revisions. The other overfished stock, cowcod, continues to have a
positive rebuilding outlook, and no changes to its rebuilding plan are
proposed. Therefore, this rule proposes to establish harvest
specifications consistent with the existing rebuilding plan provisions
for this stock. Since the 2017-18 biennium, three stocks have been
declared rebuilt: Darkblotched rockfish, bocaccio rockfish (bocaccio),
and Pacific ocean perch. The harvest control rules for these stocks
revert back to those established prior to the stock being declared
overfished.
To keep mortality of the stocks managed under the PCGFMP within the
ACLs, the Council also recommended management measures. Generally
speaking, management measures are intended to rebuild overfished
stocks, prevent catch from exceeding the ACLs, and allow for the
harvest of healthy stocks. Management measures include time and area
restrictions, gear restrictions, trip or bag limits, size limits, and
other management tools. Management measures may vary by fishing sector
because different fishing sectors require different types of management
to control catch. Most of the management measures the Council
recommended for 2019-20 were slight variations to existing management
measures, and do not represent a change from current management
practices. Additionally, the Council recommended several new management
measures, including: Establishment of salmon bycatch mitigation
measures, modifications to depth restrictions in the Western Cowcod
Conservation Area (CCA), modification of discard mortality rates for
IFQ lingcod and sablefish, removal of the Shorebased Individual Fishing
Quota (IFQ) Program daily vessel limits, removal of the automatic
authority on at-sea set-asides, continuation of the IFQ adaptive
management pass through, and modification of the retention ratios for
incidentally caught lingcod in the salmon troll fishery.
Table of Contents
I. Background
A. Specification and Management Measure Development Process
II. Harvest Specifications
A. Proposed OFLs for 2019 and 2020
B. Proposed ABCs for 2019 and 2020
C. Proposed ACLs for 2019 and 2020
D. Summary of ACL Changes From 2018 to 2019-20
III. Management Measures
A. Deductions From the ACLs
B. Stock Complex Composition Restructuring
C. Biennial Fishery Allocations
D. Tribal Fisheries
E. Routine Modifications to the Boundaries Defining Rockfish
Conservation Areas (RCAs)
F. Limited Entry Trawl
G. Limited Entry Fixed Gear and Open Access Nontrawl Fishery
H. Recreational Fisheries
I. Salmon Bycatch Mitigation Measures
J. Modifications to Depth Restrictions Within the Western CCA
K. Modification of Lingcod and Sablefish Discard Mortality Rates
L. Removal of IFQ Daily Vessel Limits
M. Removal of Automatic Authority for Darkblotched Rockfish and
Pacific Ocean Perch Set-Asides for At-Sea Sector
N. Continuation of Adaptive Management Pass Through
O. Modification of the Incidental Lingcod Retention Ratio in the
Salmon Troll Fishery
P. Administrative Actions
IV. Classification
I. Background
The PCGFMP requires the harvest specifications and management
measures for groundfish to be set at least biennially. This proposed
rule is based on the Council's final recommendations made at its June
2018 meeting, as well as harvest specifications for some stocks adopted
at the Council's April 2018 meeting.
A. Specification and Management Measure Development Process
The Northwest Fisheries Science Center (NWFSC) conducted full stock
assessments in 2017 for 9 of the 128 stocks \1\ included under the
PCGFMP (Blue/deacon rockfish (CA, WA, OR), California scorpionfish,
lingcod [north and south], Pacific ocean perch, yellowtail rockfish
north of 40[deg]10' N lat., yelloweye rockfish). Additionally, the
NWFSC conducted assessment updates that run new data through existing
models for eight stocks (arrowtooth flounder, blackgill rockfish south
of 40[deg]10' N lat., bocaccio S of 43[deg] N lat., darkblotched
rockfish). The NWFSC did not update assessments for the remaining
stocks, so harvest specifications for these stocks are based on
assessments from previous years. The stock assessment reports are
available on the Council website (https://www.pcouncil.org/).
---------------------------------------------------------------------------
\1\ Stocks for which ACLs or ACL contributions to stock complex
ACLs are calculated.
---------------------------------------------------------------------------
The Council's stock assessment review panel (STAR panel) reviews
the stock assessments, including data moderate assessments, for
technical merit, and to determine that each stock assessment document
is sufficiently complete. Finally, the SSC reviews the stock assessment
and STAR panel reports and makes recommendations to the Council.
When spawning stock biomass (B) falls below the minimum stock size
threshold (MSST), a stock is declared overfished, and the Council must
develop a rebuilding plan that sets the strategy for rebuilding the
stock to BMSY in the shortest time possible, while
considering needs of fishing communities and other factors. The current
MSST reference point for assessed flatfish stocks is 12.5 percent of
initial biomass or B12.5. For all other assessed
groundfish stocks, the current MSST reference point is 25 percent of
initial biomass or B25. The following overfished
groundfish stocks would continue be managed under rebuilding plans in
2019-20: Cowcod south of 40[deg]10' N lat. and yelloweye rockfish.
For overfished stocks, in addition to any stock assessments or
stock assessment updates, the NWFSC may also prepare rebuilding
analyses. The rebuilding analysis is used to project the future status
of the overfished resource under a variety of alternative harvest
strategies and to determine the probability of recovering to
BMSY or its proxy within a specified timeframe.
The Council considered new stock assessments, stock assessment
updates, a rebuilding analysis for yelloweye rockfish, public comment,
and advice from its advisory bodies over the course of six Council
meetings during development of its recommendations for the 2019-20
harvest specifications and management measures. At each Council meeting
between June 2017 and June 2018, the Council made a series of decisions
and recommendations that were, in some cases, refined after further
analysis and discussion. Detailed information, including the supporting
documentation the Council considered at each meeting is available at
the Council's website, www.pcouncil.org.
The 2019-20 biennial management cycle was the second cycle
following PCGFMP Amendment 24 (80 FR 12567, March 10, 2015), which
established default harvest control rules and included an Environmental
Impact Statement (EIS). The EIS described the ongoing implementation of
the PCGFMP and default harvest control rules, along with ten-year
projections for harvest specifications and a range of management
measures. Under Amendment 24, the default harvest control rules used to
determine the
[[Page 47418]]
previous biennium's harvest specifications (i.e., OFLs, ABCs, and 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 unless the Council makes a different recommendation. Therefore,
this rule implements the default harvest control rules, consistent with
Amendment 24, for most stocks, and discusses departures from the
defaults. The Analysis identifies the preferred alternative harvest
control rules, new management measures, and other decision points that
were not described in the 2015 EIS and is posted on the NMFS WCR web
page (see SUPPLEMENTARY INFORMATION) along with this proposed rule.
Information regarding the OFLs, ABCs, and ACLs proposed for
groundfish stocks and stock complexes in 2019-20 is presented below,
followed by a discussion of the proposed management measures for
commercial and recreational groundfish fisheries.
II. Harvest Specifications
This proposed rule would set 2019-20 harvest specifications and
management measures for all of the 128 groundfish stocks which 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.
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 categories to define OFLs and ABCs based on the level
of reliable information available to fishery scientists. 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 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 (DBSRA), depletion corrected average catch (DCAC), and average
catches) are used to determine the OFL for category three stocks.
A. Proposed OFLs for 2019 and 2020
The SSC derives OFLs for groundfish stocks with stock assessments
by applying the harvest rate to the current estimated biomass.
Fx harvest rates represent the rates of fishing mortality 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).
For 2019-20, the Council maintained its policy of using a default
harvest rate as a proxy for the fishing mortality rate that is expected
to achieve the maximum sustainable yield (FMSY). A proxy is
used because there is insufficient information for most Pacific Coast
groundfish stocks to estimate stock-specific FMSY values.
Taxon-specific proxy fishing mortality rates are used due to perceived
differences in the productivity among different taxa of groundfish. A
lower value is used for stocks with relatively high resilience to
fishing while higher values are used for less resilient stocks with low
productivity. In 2019-20, the Council proposed the following default
harvest rate proxies, 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),
F40 for Pacific whiting, 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.
Stocks may be grouped into complexes for various reasons,
including: When stocks in a multispecies fishery cannot be targeted
independently of one another and MSY cannot be defined on a stock-by-
stock basis; when there is insufficient data to measure the stocks'
status; or when it is not feasible for fishermen to distinguish
individual stocks among their catch. Most groundfish stocks managed in
a stock complex are data-poor stocks without full stock assessments.
The proposed OFLs for stock complexes are the sum of the OFL
contributions for the component stocks, when known. In the 2017-18
harvest specifications, there were eight stock complexes used to manage
groundfish stocks pursuant to the PCGFMP. These stock complexes were:
(1) Minor Nearshore Rockfish north; (2) Minor Nearshore Rockfish south;
(3) Minor Shelf Rockfish north; (4) Minor Shelf Rockfish south (5)
Minor Slope Rockfish north; (6) Minor Slope Rockfish south; (7) Other
Flatfish; and (8) Other Fish. This rule proposes the following changes
to stock complexes: (1) Remove blue/deacon rockfish from the Minor
Nearshore Rockfish north complex and group with Oregon black rockfish
to create a new complex (Oregon black rockfish/blue rockfish/deacon
rockfish); (2) remove Washington kelp greenling from the Other Fish
complex and pair with Washington cabezon to create a new complex
(Washington cabezon/kelp greenling); (3) remove Oregon kelp greenling
from the Other Fish complex and pair with Oregon cabezon to create a
new complex (Oregon cabezon/kelp greenling). This proposed rule, if
approved, would increase the total of number of stock complexes from
eight to eleven.
A detailed description of the scientific basis for all of the SSC-
recommended OFLs proposed in this rule is included in the Stock
Assessment and Fishery Evaluation (SAFE) document for 2018, available
at the Council's website, www.pcouncil.org.
B. Proposed ABCs for 2019 and 2020
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
establish the ABC. 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.
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
[[Page 47419]]
uncertainty beyond the sigma value reduction. The PCGFMP specifies that
the upper limit of P* will be 0.45. In combination, the P* and [sigma]
values determine the amount by which the OFL will be reduced to
establish the SSC-endorsed ABC.
The SSC quantified major sources of scientific uncertainty in the
estimates of OFLs and generally recommended a [sigma] value of 0.36 for
category one stocks, a [sigma] value of 0.72 for category two stocks,
and a [sigma] value of 1.44 for category three stocks. For category two
and three stocks, there is greater scientific uncertainty in the OFL
estimate because the assessments for these stock assessments 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 quantitative stock assessments.
Assuming the same P* is applied, a larger [sigma] value results in a
larger reduction from the OFL. For 2019-20, the Council continued the
general policy of using the SSC-recommended [sigma] values for each
stock category. However, the SSC made a few exceptions to the standard
[sigma] values assigned to each category. For some stocks, the SSC did
not deem the proxy [sigma] values the best scientific information
available because the uncertainty in estimated spawning biomass is
greater than the [sigma] used as a proxy for other stocks in that
category. For 2019-20, the SSC calculated unique [sigma] values for
five stocks. For kelp greenling off Oregon, a category 1 stock, the SSC
calculated a [sigma] value of 0.44, which is more precautionary than
the standard [sigma] value of 0.36 for this category of stocks. For
aurora rockfish, also a category 1 stock, the SSC calculated a [sigma]
value of 0.39. And for California scorpionfish, the SSC calculated a
[sigma] value of 0.582. The SSC also calculated a [sigma] value of
0.783 for California blue/deacon rockfish, and a [sigma] value of 0.803
for Oregon blue/deacon rockfish, both category 2 stocks. These [sigma]
values are higher than the standard [sigma] value of 0.72 for this
category of stocks.
For 2019-20, the Council maintained the P* policies it established
for the previous biennium for most stocks. As was done in 2015-16 and
2017-18, the Council recommended using P* values of 0.45 for all
individually managed category one stock, except sablefish. Combining
the category one [sigma] value of 0.36 with the P* value of 0.45
results in a reduction of 4.4 percent from the OFL when deriving the
ABC. For category two and three stocks, the Council's general policy
was to use a P* of 0.4, with a few exceptions. The Council recommended
a P* of 0.45 for all of the stocks managed in the Minor Rockfish
complexes and the Other Fish complex, as was done in 2017-18. When
combined with the [sigma] values of 0.72 and 1.44 for category two and
three stocks, a P* value of 0.40 corresponds to 16.7 percent and 30.6
percent reductions, respectively. The Council recommended using P*
values of 0.40 for all individually managed category two and three
stocks, except those described below. The Council recommended a P* of
0.45 for big skate, black rockfish off Oregon, cowcod, English sole,
and yellowtail rockfish south of 40[deg]10' N lat., as was done in
2015-16 and 2017-18, because there was no new scientific information
indicating a change in P* value was warranted.
C. Proposed ACLs for 2019 and 2020
The Council recommends ACLs for each stock and stock complex that
is ``in the fishery'', as defined in the PCGFMP. 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 the precautionary threshold, 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. Alternatively, even if a stock
biomass is larger than BMSY, an ACL may be set below the ABC
to address conservation objectives, socioeconomic concerns, management
uncertainty, or other factors necessary to meet management objectives.
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).
Many groundfish stocks are managed with stock-specific harvest
specifications. Often these stocks are category one or category two
stocks and their stock status is known. The default harvest control
rule for stocks with biomass estimates above MSY is to set the ACL
equal to the ABC. The default harvest control rule for stocks with
biomass estimates below MSY but above the overfished threshold is to
set the ACL below the ABC using a standard reduction on the harvest
rate, which is described in the proposed and final rules for the 2015-
16 biennium (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. Both ACL harvest control rules are
applied after the ABC deduction is made. 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. These harvest
policies foster a quicker return to the BMSY level and serve
as an interim rebuilding policy for stocks that are below the MSST.
All of the ACLs for stock complexes are less than or equal to the
summed ABC contributions of each component stock in each complex.
Default harvest control rules are based on stock status. Thus, when the
Council revises the stock composition of a stock complex, the default
harvest control rule may adjust based on status of the stocks that
remain in the complex.
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. For many of the stocks or
stock complexes in the fishery, the Council chose to maintain the
default harvest control rules from the previous biennial cycle. Table 1
presents a summary table of the proposed changes to ACL policies for
certain stocks for 2019-20.
[[Page 47420]]
Table 1--Proposed Changes to Harvest Control Rules for 2019-20
----------------------------------------------------------------------------------------------------------------
Stock Alternative Harvest control rule ACL \a\
----------------------------------------------------------------------------------------------------------------
CA Scorpionfish S of 34[deg]27' N Current............................ 150 mt constant catch 150 mt
lat. Proposed change.................... ACL. 313 mt
ACL = ABC (P* = 0.45)...
Lingcod N of 40[deg]10' N lat.... Current............................ ACL = ABC (P* = 0.45 in 3,110 mt
OR & WA; P* = 0.4 in
CA) w/40-10 adj. for
the CA contribution to
the ABC and ACL Assumes
1,000 mt and 750 mt
removals for 2017 and
2018 in the north and
south, respectively and
full ACL attainment
thereafter.
Proposed change.................... ACL = ABC (P* = 0.45) w/ 4,871 mt
40-10 adj. for the CA
contribution to the ABC
and ACL Assumes 40% and
75% ACL attainment for
2017 and 2018 in the
north and south,
respectively and full
ACL attainment
thereafter.
Lingcod S of 40[deg]10' N lat.... Current............................ ACL = ABC (P* = 0.4) w/ 1,144 mt
40-10 adj. Assumes
1,000 mt and 750 mt
removals for 2017 and
2018 in the north and
south, respectively and
full ACL attainment
thereafter.
Proposed change.................... ACL = ABC (P* = 0.45) w/ 1,039 mt
40-10 adj. Assumes 40%
and 75% ACL attainment
for 2017 and 2018 in
the north and south,
respectively and full
ACL attainment
thereafter.
Yelloweye Rockfish............... Current............................ ABC (P* = 0.4), ACL (SPR 20 mt
Proposed change.................... = 76.0%); TTARGET = 48 mt
2027.
ABC (P* = 0.4), ACL (SPR
= 65.0%); TTARGET =
2029.
----------------------------------------------------------------------------------------------------------------
\a\ Current ACL is for 2018, Proposed change ACL is for 2019.
The following sections discuss proposed ACLs for the stocks for
which the Council's recommended ACLs depart from the existing default
harvest control rule.
California Scorpionfish
For the 2017-18 biennium, the default harvest control rule set the
ACL for California scorpionfish at a constant value of 150 mt rather
than on a rate-based value. The NWFSC conducted a new assessment of
California scorpionfish south of 34[deg]27' N lat. in 2017. The
assessment indicated the stock was healthy at a 54 percent depletion at
the start of 2017. The Council recommended and NMFS is proposing an
alternative harvest control rule for California scorpionfish. The
revised harvest control rule would set the ACL equal to the ABC using a
P* value of 0.45, consistent with other category one stocks. The
resulting 2019-20 ACLs would more than double compared to the 2018 ACL
under this new harvest control rule. The stock is projected to remain
healthy (i.e., greater than 40 percent depletion) for the next ten
years under the proposed alternative harvest control rule.
Lingcod
The NWFSC conducted two assessments for lingcod in 2017--one each
for the areas north and south of the California/Oregon border at
42[deg] N lat. Current spawning stock biomass is estimated to be 57.9
percent in the northern assessment area relative to unfished spawning
biomass, and has continued to increase over the last five years as a
result of high recruitment in 2008 and 2013. Current spawning stock
biomass is estimated to be 32.1 percent in the southern assessment area
relative to unfished spawning biomass. Although spawning biomass in the
southern assessment area is estimated to have been increasing in recent
years, recruitment is estimated to have been well below average over
the last 10 to 15 years, which suggests that stock biomass is not
increasing for the southern portion of the stock at the same rate as
for the northern portion of the stock. The SSC endorsed the 2017 north
and south lingcod stock assessments as the best scientific information
available for status determination and management, and designated both
portions of the stock as category one. The stocks had been previously
managed as category two stocks. The current harvest control rule sets
the ACL equal to the ABC for the portion of the northern stock off
Oregon, but applies the 40-10 precautionary reduction to the portion of
the northern stock off California (i.e., between 42[deg] and 40[deg]10'
N lat.), and to the whole of the southern stock using the most recent
5-year (2012-2016) average percentage of swept area biomass estimates.
This proposed rule would change the P* value from 0.4 to 0.45 for
both portions of the stock, reflecting greater confidence in the
current stock assessments. The resulting 2019 and 2020 ACLs for the
northern portion of the stock would increase by approximately 64
percent and 68 percent, respectively, compared to the 2018 ACL under
this new harvest control rule. The resulting 2019 and 2020 ACL under
this new harvest control rule for the southern portion of the stock
would decrease by approximately 9 percent and 24 percent, respectively,
compared to the 2018 ACL. This proposed action is expected to allow
moderate growth of the stock under an average recruitment assumption in
the next ten years.
Overfished Stocks and Changes to 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
discusses several previously overfished stocks that have rebuilt since
the last biennium, as well as provisions for the two remaining
overfished stocks in the PCGFMP, namely cowcod south of 40[deg]10' N
lat. and yelloweye rockfish. The Council proposed cowcod ACLs for 2019
and 2020 based on the current cowcod 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 history of each
overfished stock, and can be found at https://www.pcouncil.org/groundfish/fisherymanagement-plan/.
[[Page 47421]]
Stocks Rebuilt Since Last Biennium
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 2019-20 biennium, three stocks were declared
rebuilt: Bocaccio, Pacific ocean perch, and darkblotched rockfish. In
addition to the harvest control rules for these stocks reverting back
to the defaults for the 2019-20 biennium, other requirements for
overfished stocks are removed. One such change is that these stocks
would no longer be listed under the priority stock observer reporting
requirements at Sec. 660.140(h)(1)(i)(3). This proposed change is
described further under the heading, P. Administrative Actions, in this
preamble.
Yelloweye Rockfish (Sebastes Ruberrimus)
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. The current
rebuilding plan parameters include an SPR harvest rate of 76 percent
and a median target time for rebuilding (TTARGET) of 2074
(the year for which there is a 50 percent probability that the stock is
rebuilt). The NWFSC conducted a new stock assessment for yelloweye
rockfish in 2017, and the SSC conducted a rebuilding analysis using the
updated assessment. The rebuilding analysis includes a recalculation of
rebuilding parameters that inform the Council's decision-making
process. According to the rebuilding analysis, should the Council
decide to revise the existing rebuilding plan, the new minimum time to
rebuild (TMIN; the time to rebuild if there was no fishing)
would be 2026 and TTARGET would be changed from 2074 (in the
2011 assessment) to 2027 (in the 2017 assessment). Under the current
harvest control rule, the ACL for yelloweye would increase to 29 mt and
30 mt in 2019 and 2020, respectively, an increase from 20 mt in 2018.
This improvement in stock status outlook is due to several factors,
including: Lower than expected catches of yelloweye rockfish in recent
years; a more optimistic value on stock recruit steepness, which
corresponds to a more productive stock; and strong year classes
entering the spawning population in recent years.
As a result of the improvement in stock outlook, the Council
recommended, and NMFS is proposing, changing the SPR harvest rate for
yelloweye rockfish to 65 percent and changing the TTARGET to
2029. This change in the rebuilding plan would allow an ACL for
yelloweye rockfish of 48 mt in 2019 and 49 mt in 2020. Within the ACL,
for 2019, the Council recommended a fishery harvest guideline (HG) of
42.1 mt, of which 3.4 mt is the trawl HG and 38.6 mt is the nontrawl
HG. For 2020, NMFS proposes a fishery HG of 42.1 mt, of which 3.4 is
the trawl HG and 39.5 is the nontrawl HG. For more discussion of the
use of HGs, see section II (Harvest Specifications), C, entitled ``C.
Biennial Fishery Allocations'' in this preamble.
Additionally, the Council recommended, and NMFS is proposing, to
establish Annual Catch Targets (ACTs) within the nontrawl allocation
HG. The nontrawl sector includes the limited entry fixed gear and open
access fixed gear 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. Table 2 outlines the harvest specifications that were in place
for yelloweye rockfish for 2018 for comparison purposes. Tables 3 and 4
outline the proposed harvest specifications for 2019 and 2020 for
yelloweye rockfish.
Table 2--2018 Harvest Specifications for Yelloweye Rockfish
----------------------------------------------------------------------------------------------------------------
OFL (mt) ABC (mt) ACL (mt) HG (mt)
----------------------------------------------------------------------------------------------------------------
All sectors..................................... 58 48 20 14
Nontrawl.................................... .............. .............. .............. 12.9
Non-Nearshore........................... .............. .............. .............. 0.7
Nearshore............................... .............. .............. .............. 2.0
Washington Recreational................. .............. .............. .............. 3.3
Oregon Recreational..................... .............. .............. .............. 3
California Recreational................. .............. .............. .............. 3.9
Trawl....................................... .............. .............. .............. 1.1
----------------------------------------------------------------------------------------------------------------
Table 3--2019 Harvest Specifications for Yelloweye Rockfish
----------------------------------------------------------------------------------------------------------------
OFL (mt) ABC (mt) ACL (mt) HG (mt) ACT (mt)
----------------------------------------------------------------------------------------------------------------
All sectors..................... 82 74 48 42 ..............
Nontrawl.................... .............. .............. .............. 38.6 ..............
Non-Nearshore........... .............. .............. .............. 2.0 1.6
Nearshore............... .............. .............. .............. 6.0 4.7
Washington Recreational. .............. .............. .............. 10.0 7.8
Oregon Recreational..... .............. .............. .............. 8.9 7.0
California Recreational. .............. .............. .............. 11.6 9.1
Trawl....................... .............. .............. .............. 3.4 ..............
----------------------------------------------------------------------------------------------------------------
Table 4--2020 Harvest Specifications for Yelloweye Rockfish
----------------------------------------------------------------------------------------------------------------
OFL (mt) ABC (mt) ACL (mt) HG (mt) ACT (mt)
----------------------------------------------------------------------------------------------------------------
All sectors..................... 84 77 49 43 ..............
[[Page 47422]]
Nontrawl.................... .............. .............. .............. 39.5 ..............
Non-Nearshore........... .............. .............. .............. 2.1 1.7
Nearshore............... .............. .............. .............. 6.2 4.9
Washington Recreational. .............. .............. .............. 10.2 8.1
Oregon Recreational..... .............. .............. .............. 9.1 7.2
California Recreational. .............. .............. .............. 11.9 9.4
Trawl....................... .............. .............. .............. 3.4 ..............
----------------------------------------------------------------------------------------------------------------
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
how encounter rates will change under the proposed higher catch limits
and the associated suite of management measures that should allow for
an overall expansion of groundfish fishery effort (see section 4.2.1.3
of the Analysis). 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
overfished stock by this sector.
The Analysis demonstrates how the proposed changes to the
rebuilding plan select a TTARGET that is as short as
possible, while giving consideration to the status and biology of the
overfished species and the needs of the fishing communities, consistent
with Section 303(e)(4) of the Magnuson-Stevens Act (see Appendix B of
the Analysis). The Council indicated that a new default harvest control
rule may more appropriately account for the needs of West Coast
communities by providing greater opportunity in both commercial and
recreational groundfish sectors and improving income stability for
dependent communities.
West Coast fishing communities depend on a portfolio of commercial
and recreational fisheries to support year-round operations. Recent
coastwide declines in commercial fisheries for Dungeness crab, salmon,
sardines, tuna, pink shrimp, halibut, and other non-groundfish stocks
due to changing environmental conditions and changes in management have
created considerable instability for many communities. Additionally,
many of these communities have experienced substantial declines in
recreational fishing activity, notably for salmon and for tuna (see
Section B.1.1. of Appendix B). Groundfish fishing activity has
traditionally helped communities weather cyclical changes in abundance
in other non-groundfish fisheries. However, the restrictions in catch
of target groundfish stocks necessary to support rebuilding of
overfished groundfish stocks over the past 15 years has limited both
commercial and recreational groundfish fishing opportunities. The loss
of groundfish fishing opportunities further affects fishing communities
through loss of processor activity and loss of business for support
services.
The proposed change to the yelloweye rockfish rebuilding plan is
intended to support continued yelloweye rebuilding progress while
providing more stability for coastal communities through increased
access to co-occurring target stocks. Yelloweye rockfish bycatch is
rare and unpredictable, but can occur in sporadic ``lightning strikes''
of large magnitude. Because yelloweye rockfish catch is difficult to
predict, the Council has constrained yelloweye rockfish catch below the
ACL set in the current rebuilding plan by conservatively managing co-
occurring target stocks. This proposed rebuilding plan would increase
the estimated TTARGET by two years, from 2027 to 2029, which
is still within the required 10-year rebuilding timeframe specified in
section 304(e)(4) of the Magnuson-Stevens Act, but which would more
than double the yelloweye rockfish ACL in 2019 compared to 2018.
The higher ACLs resulting from the revised rebuilding plan allow a
suite of management measures that could expand groundfish fishing
opportunities. For commercial trawl vessels, this proposed action would
facilitate more trading of yelloweye rockfish allocation, which should
allow for less risk-averse fishing strategies and as a result, an
increase in attainment of underutilized stocks, including lingcod,
chilipepper rockfish, and Pacific cod (see Section B.5.2.3 of Appendix
B of the Analysis). For commercial fixed gear vessels, the yelloweye
rockfish ACL increases could support future actions to consider
reopening the nontrawl Rockfish Conservation Area or to consider
increasing trip limits for target stocks such as lingcod (see Section
B.5.2.2 of Appendix B of the Analysis). In addition, the proposed
increases in the yelloweye rockfish ACL would allow for additional
research opportunities to collect much-needed data to better inform
stock assessments and management decisions (see Section B.1.3 of
Appendix B of the Analysis).
Recreational fishing opportunities would have the greatest
potential for expansion from this proposed action. For the recreational
sectors in communities off Washington, Oregon, and California, the
proposed change to the rebuilding plan and higher ACLs would allow
shorter periods of time with depth restrictions in place and access to
deeper depths during seasons with depth restrictions. Allowing
recreational fishermen to access additional fishing grounds should
allow them to target a broader suite of stocks, such as yellowtail
rockfish, lingcod, and chilipepper rockfish, while also reducing
pressure on sensitive nearshore stocks such as black rockfish (see
Section B.5.3 of Appendix B of the Analysis). This increase in
recreational effort would especially benefit the communities of Neah
Bay, WA; Winchester Bay, OR; and Fort Bragg, CA, which are highly
dependent on recreational opportunities (see Section B.5 of Appendix B
of the Analysis).
D. Summary of ACL Changes From 2018 to 2019-20
Table 5 compares the ACLs for major stocks for 2018, 2019, and
2020. Due to proposed changes in stock complex composition, not all
stocks are shown below. Many stocks would have higher ACLs in 2019 and
2020 than in 2018. The only stock that would have an ACL more than 10
percent below the 2018 ACL is starry flounder. The change in stock
abundance for starry flounder is largely driven by a change in the way
the stock is assessed, which better accounts for the uncertainty in the
stock status of this data poor stock. As a result, for 2019-20, starry
flounder has a more precautionary OFL, ABC, and ACL. Overall attainment
of starry flounder has been low in recent years, so this change is not
expected to have
[[Page 47423]]
a substantial impact on the fleet (see Section A.3.4 of Appendix A of
the Analysis).
Table 5--ACLs for Major Stocks for 2018, 2019, and 2020
[Overfished stocks are capitalized]
----------------------------------------------------------------------------------------------------------------
Percent change
Stock Area 2018 ACL (mt) 2019 ACL (mt) 2020 ACL (mt) 2018 to 2019
----------------------------------------------------------------------------------------------------------------
COWCOD........................ S of 40[deg]10' 10 10 10 0
N lat.
YELLOWEYE ROCKFISH............ Coastwide....... 20 48 49 140
Arrowtooth Flounder........... Coastwide....... 13,743 15,574 12,750 13
Big Skate..................... Coastwide....... 494 494 494 0
Black Rockfish................ California (S of 332 329 326 -1
42[deg] N lat.).
Black Rockfish................ Washington (N of 301 298 297 -1
46[deg]16' N
lat.).
Bocaccio a.................... S of 40[deg]10' 741 2,097 2,011 183
N lat.
Cabezon....................... California (S of 149 147 146 -1
42[deg] N lat.).
California Scorpionfish....... S of 34[deg]27' 150 313 307 108
N lat.
Canary Rockfish............... Coastwide....... 1,526 1,450 1,368 -5
Chilipepper Rockfish.......... S of 40[deg]10' 2,507 2,536 2,410 1
N lat.
Darkblotched Rockfish a....... Coastwide....... 653 765 815 17
Dover Sole.................... Coastwide....... 50,000 50,000 50,000 0
English Sole.................. Coastwide....... 7,537 10,090 10,135 34
Lingcod....................... N of 40[deg]10' 3,110 4,871 4,541 57
N lat.
Lingcod....................... S of 40[deg]10' 1,144 1,039 869 -9
N lat.
Longnose skate................ Coastwide....... 2,000 2,000 2,000 0
Longspine Thornyhead.......... N of 34[deg]27' 2,747 2,603 2,470 -5
N lat.
Longspine Thornyhead.......... S of 34[deg]27' 867 822 780 -5
N lat.
Pacific Cod................... Coastwide....... 1,600 1,600 1,600 0
Pacific Ocean Perch a......... N of 40[deg]10' 281 4,340 4,229 1444
N lat.
Petrale Sole.................. Coastwide....... 3,013 2,908 2,845 -3
Sablefish..................... N of 36[deg] N 5,475 5,606 5,723 2
lat.
Sablefish..................... S of 36[deg] N 1,944 1,990 2,032 2
lat.
Shortbelly Rockfish........... Coastwide....... 500 500 500 0
Shortspine Thornyhead......... N of 34[deg]27' 1,698 1,683 1,669 -1
N lat.
Shortspine Thornyhead......... S of 34[deg]27' 898 890 883 -1
N lat.
Spiny Dogfish................. Coastwide....... 2,083 2,071 2,059 -1
Splitnose Rockfish............ S of 40[deg]10' 1,761 1,750 1,731 -1
N lat.
Starry Flounder............... Coastwide....... 1,282 452 452 -65
Widow Rockfish................ Coastwide....... 12,655 11,831 11,199 -7
Yellowtail Rockfish........... N of 40[deg]10' 6,002 5,997 5,716 0
N lat.
----------------------------------------------------------------------------------------------------------------
a Stock was declared rebuilt in 2017.
III. Management Measures
This section describes biennial fishery harvest guidelines and set-
asides used to further allocate the ACLs to the various components on
the fishery, routine management measures to control fishing, and new
management measures proposed for 2019-20. Routine management measures
for the commercial fishery modify fishing behavior during the fishing
year to ensure that catch is constrained below the ACL, and include
trip and cumulative landing limits, time/area closures, size limits,
and gear restrictions. Routine management measures for the recreational
fisheries include bag limits, size limits, gear restrictions, fish
dressing requirements, and time/area closures. New management measures
proposed for the 2019-20 biennial cycle would work in combination with
current management measures to control fishing effort/activity.
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 set aside
fish for certain types of activities. Off the top deductions account
for four distinct sources of groundfish mortality: 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 exempted fishing permits (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.
B. Stock Complex Composition Restructuring
The Council recommended, and NMFS is proposing, modifications to
the existing stock complexes used for harvest specifications and
management that would create three new stock complexes. Changes in the
composition of stock complexes do not affect the underlying harvest
specifications because the stock complex ACL is simply the sum of the
constituent stocks' specifications. The stocks in the proposed stock
complex restructuring are predominately shallow water nearshore stocks
that occur primarily within state waters. Nearly all the removals for
these stocks are attributed to the recreational and commercial
nearshore fisheries that are subject to joint state and Federal
management.
The first modification would remove Oregon blue/deacon rockfish
(BDR) from the Nearshore Rockfish complex north of 40[deg]10' N
latitude and pair it with Oregon black rockfish to form a new Oregon
black/BDR complex. The second modification would remove Oregon and
Washington kelp greenling and Washington cabezon from the Other Fish
complex to form two new stock complexes: An Oregon Kelp Greenling/
[[Page 47424]]
Cabezon Complex and a Washington Kelp Greenling/Cabezon Complex. The
objectives of the stock complex proposals are: (1) Better alignment of
stocks per the complex goals and definitions as defined in the PCGFMP
and National Standard 1 of the Magnuson-Stevens Act; (2) reduced
management complexity; and 3) enhanced management flexibility (e.g.,
greater ability to take inseason actions). These proposed changes to
stock complex composition better comply with the National Standard 1
guidelines, which recommend stocks managed in a stock complex ``should
have a similar geographic distribution, life history characteristics,
and vulnerabilities to fishing pressure such that the impact of
management actions on the stocks is similar.'' These complex proposals
pertain primarily to the commercial nearshore and recreational
fisheries, as these are shallow water stocks infrequently encountered
by the trawl sectors or other fisheries.
Oregon Black/Blue/Deacon Rockfish Complex
The Council recommended removing Oregon BDR rockfish from the
Nearshore Rockfish complex north of 40[deg]10' N. latitude, and pairing
it with Oregon black rockfish, which is currently managed individually,
to form a new Oregon black/BDR complex. Note that blue and deacon
rockfish are separate stocks, but they are referred to collectively
since they were assessed together and therefore have joint harvest
specifications. Blue/deacon rockfish are more frequently found in the
middle of the water column, whereas the other stocks in the Nearshore
Rockfish complex are more strongly associated with benthic habitats.
Oregon black rockfish is an important target fishery, especially in the
recreational sector. As detailed in Section C.3 of Appendix C of the
Analysis, this proposed action would better align management of Oregon
BDR rockfish with black rockfish, a stock that is also a midwater stock
and often co-occurs with BDR rockfish. The proposed action would
provide more targeted management of Oregon BDR rockfish by moving
Oregon BDR from a larger stock complex to a much smaller one. However,
this action could have the potential to provide less targeted
management for black rockfish by moving it from individual management
into a complex. The risk of less targeted management would be that
catch could exceed the stock's ACL contribution while remaining under
the overall complex ACL.
As a measure to prevent negative effects on black rockfish as a
result of moving it into a complex, the Council recommended and NMFS is
proposing an HG for the stock at its ACL contribution level to the
complex. For 2019, the HG would be 515.8 mt, and for 2020, 512.2 mt.
Additionally, as discussed in Section 4.3.1.3 of the Analysis, Oregon
Department of Fish and Wildlife (ODFW) intends to implement mitigation
measures to prevent any change in the risk of overfishing for Oregon
black rockfish. These measures include establishing and managing catch
against state harvest guidelines for the component stocks of the new
BDR complex, shortening the state catch reporting time lag from one
month to one week to allow for rapid state-level management response,
and revising ODFW inseason catch projection methods to better monitor
rapid periodic increases in recreational fishing effort. ODFW has also
proposed action within its state regulations to reduce its aggregate
state recreational bag limit from seven to five fish per day, which
could slow the overall catch rate during the recreational season.
Finally, NMFS's recent approval of longleader fishing gear for use in
waters off Oregon (83 FR 13428; March 29, 2018) could shift some
fishing effort away from black rockfish and towards underutilized
midwater stocks, primarily widow and yellowtail rockfish. If this
change to the stock complex structure is approved, these additional
measures would ensure a level of management scrutiny for black rockfish
similar to the level it would receive if it were managed individually.
Other Fish Complex
The Other Fish complex originated as a compilation of stocks that
did not match well with other complexes. Because the complex is
composed of biologically dissimilar stocks (e.g., ratfish, skates,
sharks, grenadier, greenling, cabezon, and codling), the grouping has
not supported practical management of its component stocks. Over time,
the Council has redesignated some stocks in the original complex as
ecosystem components, or has removed some stocks from the complex for
individual management (e.g., big skate, 82 FR 9634; February 7, 2017).
This proposed action would remove three stocks from the Other Fish
complex and incorporate them into two new complexes to allow for more
accurate management of these stocks. This action would also require the
addition of scientific sorting requirements for the limited entry
trawl, limited entry fixed gear, and open access fixed gear. These
sorting requirements would allow proper accounting of the catch of
component stock in these new complexes separate from the Other Fish
complex.
Oregon Kelp Greenling/Cabezon Complex
This proposed action would remove Oregon kelp greenling from the
Other Fish complex and pair it with Oregon cabezon, which is currently
managed individually, to create the Oregon Kelp Greenling/Cabezon
Complex. This proposed action was recommended because these stocks
share a greater similarity to each other (e.g., both are solitary
nearshore stocks that often co-occur) compared to the other stocks
within the Other Fish complex. As a measure to prevent any increase in
the risk of overfishing for cabezon as a result of moving it into a
complex, the Council recommended and NMFS is proposing a HG for the
stock at its ACL contribution level to the complex. For 2019 and 2020,
the HG would be 46.8 mt. The mitigation measures ODFW intends to
implement for the Oregon black/BRD complex, described above, would
similarly help prevent adverse effects on cabezon from moving from
individual management into a stock complex.
Washington Kelp Greenling/Cabezon Complex
This proposed action would remove Washington kelp greenling and
Washington cabezon from the Other Fish complex to form a Washington
Kelp Greenling/Cabezon Complex. In Washington, kelp greenling and
cabezon are retained in recreational groundfish fisheries. They are
nearshore stocks that are generally not targeted and often co-occur. As
both of the stocks are currently managed within a larger complex,
moving them to their own complex would provide more targeted
management. As part of this proposed action, the Washington Department
of Fish and Wildlife would be better able to implement inseason
management actions for these stocks, if needed.
C. Biennial Fishery Allocations
The Council recommends two-year trawl and nontrawl allocations
during the biennial specifications process for all stocks without long-
term allocations or stocks where the long-term allocation is suspended
because the stock is declared overfished. For all stocks, except
sablefish north of 36[deg] N lat., the Council recommends allocations
for the trawl and nontrawl sectors 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
[[Page 47425]]
(Management Measures), A, entitled ``Deductions from the ACLs,'' in
this preamble. The two-year allocations and recreational harvest
guidelines are designed to accommodate anticipated mortality in each
sector as well as variability and uncertainty in those mortality
estimates. 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.
Big Skate
The Council recommended and NMFS is proposing the allocations shown
in Table 6 for big skate in 2019 and 2020. These allocations are
anticipated to accommodate estimates of mortality of big skate, by
sector, in 2019-20.
Table 6--2019 and 2020 Trawl/Nontrawl Allocations of Big Skate
------------------------------------------------------------------------
Allocation
Percentage (mt)
------------------------------------------------------------------------
Nontrawl................................ 5 22.6
Trawl................................... 95 429.5
------------------------------------------------------------------------
Bocaccio
Bocaccio was declared rebuilt since last biennium. The Council
recommended and NMFS is proposing the allocations shown in Table 7 for
bocaccio in 2019 and 2020. These allocations are anticipated to
accommodate estimates of mortality of bocaccio, by sector, in 2019-20
and address the stock's newly rebuilt status.
Table 7--2019 and 2020 Allocations of Bocaccio
------------------------------------------------------------------------
2019 HG (mt) 2020 HG (mt)
------------------------------------------------------------------------
Trawl................................... 800.7 767.1
Non-nearshore........................... 382.0 366.0
Nearshore............................... 4.8 4.6
California recreational................. 863.4 827.2
------------------------------------------------------------------------
Canary Rockfish
The Council recommended and NMFS is proposing the allocations in
Table 8 for canary rockfish in 2019 and 2020. These allocations are
anticipated to accommodate estimates of mortality of canary rockfish,
by sector, in 2019-20, and maintain the same allocation scheme as in
2018.
Table 8--2019 and 2020 Allocations of Canary Rockfish
------------------------------------------------------------------------
2019 HG (mt) 2020 HG (mt)
------------------------------------------------------------------------
Shorebased IFQ Program.................. 953.6 894.3
At-sea Sectors.......................... 46 46
Catcher/processor................... 16 16
Mothership.......................... 30 30
Non-nearshore........................... 43.8 41.2
Nearshore............................... 94.3 88.7
Washington recreational................. 47.1 44.3
Oregon recreational..................... 70.7 66.5
California recreational................. 127.3 119.7
------------------------------------------------------------------------
Cowcod
For 2019-20, the Council recommended and NMFS is proposing setting
a cowcod ACT at 6 mt, and having it function as a fishery harvest
guideline similar to the ACT in the 2017-18 biennium; it is the amount
that would be allocated across groundfish fisheries. Table 9 shows the
trawl/nontrawl allocations for cowcod for 2019 and 2020. NMFS
anticipates the proposed allocation structure will keep catch below the
2019-20 cowcod ACT, and NMFS maintains the same allocation scheme as in
2018.
Table 9--2019 and 2020 Trawl/Nontrawl Allocations of Cowcod
------------------------------------------------------------------------
Allocation
Percentage (mt)
------------------------------------------------------------------------
Nontrawl................................ 36 2.2
Trawl................................... 64 3.8
------------------------------------------------------------------------
[[Page 47426]]
Longnose Skate
The Council recommended and NMFS is proposing the trawl/nontrawl
allocations for longnose skate in Table 10. The allocation percentages
reflect historical catch of longnose skate in the two sectors, and NMFS
maintains the same allocation scheme that was in place for longnose
skate in 2018.
Table 10--2019 and 2020 Trawl/Nontrawl Allocations of Longnose Skate
------------------------------------------------------------------------
Allocation
Percentage (mt)
------------------------------------------------------------------------
Nontrawl................................ 10 185.2
Trawl................................... 90 1,666.5
------------------------------------------------------------------------
Minor Nearshore Rockfish
Harvest specifications for Minor Nearshore Rockfish north of
40[deg]10' N lat. are proposed to decrease from the 103.2 mt in 2017-18
to 81 mt in 2019 and 92 mt in 2020 due to the proposed removal of
Oregon black rockfish from the complex.
The states intend to manage catch using state-specific harvest
guidelines: 18.6 mt for Washington; 23.2 mt for Oregon, and 36.6 mt for
California for 2019. For 2020, 18.3 mt for Washington; 23.0 mt for
Oregon, and 37.9 mt for California. However, instead of implementing
state specific harvest guidelines in Federal regulations, the state
Council representatives from Oregon and Washington committed to
heightened inseason communication regarding catches of stocks managed
in the complex, relative to the harvest guidelines, consistent with the
current state coordinated management. Under state management, landed
component stocks within the Minor Nearshore Rockfish complex must be
sorted by stock. Because the states may also take inseason action
independent of NMFS, the proposed action is not anticipated to result
in exceeding the complex ACL in 2019-20.
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 2019 and 2020 are shown in Table 12. This maintains the same
allocation percentages as have been in place for the Minor Shelf
Rockfish complexes since 2011.
Table 12--Trawl/Nontrawl Allocations for Minor Shelf Rockfish North and South of 40[deg]10' N lat.
----------------------------------------------------------------------------------------------------------------
Percentage 2019 HG 2020 HG
----------------------------------------------------------------------------------------------------------------
Minor Shelf Rockfish north of Trawl................... 60.2 1,190 1,186.6
40[deg]10' N lat. Nontrawl................ 39.8 786.9 784.5
Minor Shelf Rockfish south of Trawl................... 12.2 188.6 188.6
40[deg]10' N lat. Nontrawl................ 87.8 1,357.3 1,357.3
----------------------------------------------------------------------------------------------------------------
Minor Slope Rockfish
Minor Slope Rockfish were allocated between the trawl and nontrawl
fisheries in PCGFMP Amendment 21. This action applies those Amendment
21 allocation percentages to the updated 2019-20 fishery harvest
guidelines. Blackgill rockfish in California was assessed in 2011 and
has continued to be managed within the Minor Slope Rockfish complex,
but with a stock-specific HG south of 40[deg]10' N lat. beginning in
2013. For 2019-20 the Council recommended a blackgill rockfish harvest
guideline equal to the ABC contribution for the portion of the stock
south of 40[deg]10' N lat.; this harvest guideline is 159 mt for 2019
and 2020.
D. Tribal Fisheries
Tribes implement management measures for Tribal fisheries both
independently as sovereign governments and cooperatively with the
management measures in the Federal regulations. The Tribes may adjust
their Tribal fishery management measures inseason to stay within the
Tribal harvest targets and estimated impacts to overfished stocks. The
only change to Tribal harvest targets and management measures proposed
for the 2019-20 biennium is an increase in the petrale sole harvest
target from 220 mt to 290 mt.
The Tribes proposed trip limit management in Tribal fisheries for
2019-20 for several stocks, including several rockfish stocks and stock
complexes. This rule proposes maintaining the same trip limits for
Tribal fisheries as those in place in 2018. For rockfish stocks, Tribal
regulations will continue to require full retention of all overfished
rockfish stocks and marketable non-overfished rockfish stocks. The
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.
E. Routine Modifications to the Boundaries Defining 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 2019-20 biennium, the Council recommended minor adjustments
to the 75 fathom (fm) (137 m), 100 fm (183 m), 125 fm (229 m), and 150
fm (274 m) depth contours off of California to more accurately refine
the depth contours. These proposed modifications would adjust
boundaries for RCAs around Santa Cruz Island, Spanish Canyon, Delgada
Canyon, Cordell Bank, Point Ano Nuevo, San Miguel Island, and Anacapa
Island.
Additionally, this proposed rule would correct the coordinates for
the 125 fm (229 m) depth contour recommended by the Council in June
2017 around Usal Canyon and Noyo Canyon. The Council recommended
[[Page 47427]]
these modifications to fix errors that were discovered during a
previous change to the RCA line from 150 fm (274 m) to 125 fm (229 m)
as part of the 2017-18 harvest specifications and management measures
(82 FR 9634; February 7, 2017). When NMFS implemented changes to the
RCA line, it was determined that the latitude and longitude coordinates
for several areas were crossed over between 125 and 150 fathoms. These
proposed changes would provide access to canyons that were previously
open when the 150 fm (274 m) line was in effect, and which were
intended to be open after the previous changes to the RCA line.
F. Limited Entry Trawl
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 stocks except big skate, this rule proposes maintaining the same
IFQ fishery trip limits for these stocks for the start of the 2019-20
biennium as those in place in 2018. For big skate, the Council proposes
reverting trip limits to those implemented at the start of the 2017-18
biennium. 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 are considered a routine measure
under Sec. 660.60(c), and may be implemented or adjusted, if
determined necessary, through inseason action.
G. Limited Entry Fixed Gear and Open Access Nontrawl Fishery
Management measures for the limited entry fixed gear (LEFG) and
open access (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 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
2019-20 biennium, changes to management measures include: changes to
trip limits for sablefish, minor slope rockfish and darkblotched
rockfish, canary rockfish, lingcod, shortspine rockfish, and longspine
rockfish. Proposed 2019-20 trip limits for these changes 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 raising the trip limits for the LEFG
fleet from those in 2018 between 75 to 100 lb (34 to 45 kg) a week
depending on the period of the year. For the OA fleet, the trip limits
would be the same as in 2018. For the portion south of 36[deg] N lat.,
the Council recommended the limited entry and open access trip limits
remain the same as those in 2018. The proposed sablefish trip limits
for 2019-20 are shown in Table 13.
Table 13--Sablefish Trip Limits for Limited Entry and Open Access Sectors North and South of 36[deg] N Lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
--------------------------------------------------------------------------------------------------------------------------------------------------------
Sector Area Jan-Feb Mar-Apr May-Jun Jul-Aug Sept-Oct Nov-Dec
--------------------------------------------------------------------------------------------------------------------------------------------------------
Limited entry................ north of 36[deg] 1,200 lb/week; not to exceed 3,600 lb bi-monthly.
N lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
south of 36[deg] 2,000 lb/week.
N lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Open Access.................. north of 36[deg] 300 lb daily, or one landing per week up to 1,000 lb, not to exceed 2,000 lb bi-monthly.
N lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
south of 36[deg] 300 lb daily, or 1 landing per week up to 1,600 lb, not to exceed 3,200 lb bimonthly.
N lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Minor Slope Rockfish and Darkblotched Rockfish Trip Limits
In the 2017-18 biennium, the trip limit for minor slope rockfish
and darkblotched rockfish for the OA sector was linked to the landed
weight of sablefish for the trip. The current trip limit for minor
slope rockfish and darkblotched rockfish north of 40[deg]10' N lat. is
no more than 25 percent of the landed weight of sablefish per trip,
which corresponds to a maximum of 500 lb (227 kg) bi-monthly (25
percent of the 2,000 lb (907 kg) bi-monthly limit of sablefish). This
is an aggregate limit for all stocks combined. For 2019-20, the Council
proposed and NMFS is recommending decoupling this limit from the landed
weight of sablefish and instead creating a stand-alone trip limit for
minor slope rockfish and darkblotched rockfish of 500 lb (227 kg) per
month (all stocks combined). The new limit would be double the current
limit. The Council recommended and NMFS is proposing the new trip limit
structure because it would be simpler for OA participants to abide by
and would better allow them to retain more, and discard less, of their
incidental catches.
Canary Rockfish Trip Limits
The Council recommended and NMFS is proposing that canary rockfish
retention would be permitted in the LEFG sector between 40[deg]10' N
latitude and 34[deg]27' N latitude, with a trip limit of 300 pounds per
two months. For the area south of 34[deg]27' N latitude, the trip limit
would be the same, except for a closure during Period 2 (March-April).
For OA, the structure would be similar, with a 150 lb (68 kg) per two
months limit, and a closure during Period 2 (March-April) south of
40[deg]10' N latitude. These proposed closures for the canary rockfish
trip limits would align with the trip limit structure for the Minor
Shelf Rockfish, Deeper Nearshore Rockfish, Shallow Nearshore Rockfish,
California scorpionfish, and lingcod south of 40[deg]10' N lat.
Establishing a canary rockfish bi-monthly trip limit that matches the
Shelf Rockfish trip limit would provide a uniform approach for
monitoring, management, and law enforcement. Table 14 shows the
proposed trip limits for 2019 and 2020 for canary rockfish.
[[Page 47428]]
Table 14--Proposed Canary Rockfish Trip Limits for Limited Entry and Open Access Sectors
--------------------------------------------------------------------------------------------------------------------------------------------------------
--------------------------------------------------------------------------------------------------------------------------------------------------------
Sector Area Jan-Feb Mar-Apr May-Jun Jul-Aug Sept-Oct Nov-Dec
--------------------------------------------------------------------------------------------------------------------------------------------------------
Limited entry................ N of 40[deg]10' 300 lb/2 months.
N lat.
--------------------------------------------------------------------------------------------------------------------------
40[deg]10' N 300 lb/2 months.
lat.--34[deg]27
' N lat.
--------------------------------------------------------------------------------------------------------------------------
S of 34[deg]27' 300 lb/2 months. CLOSED.......... 300 lb/2 months.
N lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Open Access.................. N of 40[deg]10' 150 lb/2 months.
N lat.
--------------------------------------------------------------------------------------------------------------------------
S of 40[deg]10' 50 lb/2 months.. CLOSED.......... 150 lb/2 months.
N lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Lingcod Trip Limits
Lingcod is managed north and south of 40[deg]10[acute] N lat. The
Council recommends OFLs, ABCs, ACLs, and HGs separately for each of
these stocks. Historically, the Council has also recommended trip
limits for LEFG and OA for each of these two stocks. For 2019-20, the
Council proposed and NMFS is recommending two separate LEFG and OA trip
limits for lingcod north of 40[deg]10[acute] N lat.: one set of trip
limits for the area north of 42[deg] N lat., and one set of trip limits
for the area between 42[deg] N lat. and 40[deg]10[acute] N lat. The new
latitude break would allow more flexibility for alternative management
strategies by state agencies to promote fishing opportunity while
staying within state-specific yelloweye rockfish shares. In addition,
this new latitude break aligns with the 42[deg] N lat. latitudinal
break used in the stock assessment (see Section A.2.6 of Appendix A of
the Analysis). This proposed rule would establish a trip limit for LEFG
of 2,000 lb (907 kg) per 2 months for the area north of 42[deg] N lat.
and a trip limit of 1,400 lb (635 kg) per 2 months for the area between
42[deg] N lat. and 40[deg]10[acute] N lat. For OA, this rule would
establish a trip limit of 900 lb (408 kg) per 2 months for the area
north of 42[deg] N lat., and a trip limit of 600 lb (272 kg) per 2
months for the area between 42[deg] N lat. and 40[deg]10[acute] N lat.
Overall, the lingcod trip limits proposed for 2019-20 are higher than
those in place in 2018, which is possible due to higher ACLs for co-
occurring yelloweye rockfish. Table 15 below shows proposed trip limits
for lingcod north of 40[deg]10[acute] N lat.
Table 15--Proposed Lingcod Trip Limits North of 40[deg]10' N Lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
--------------------------------------------------------------------------------------------------------------------------------------------------------
Sector Area Jan-Feb Mar-Apr May-Jun Jul-Aug Sept-Oct Nov-Dec
--------------------------------------------------------------------------------------------------------------------------------------------------------
Limited entry................ North of 42[deg] 2,000 lb/2 months.
N lat.
--------------------------------------------------------------------------------------------------------------------------
42[deg] N Lat. 1,400 lb/2 months.
to
40[deg]10[acute
] N lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Open access.................. N of 42[deg] N 900 lb/month.
lat.
--------------------------------------------------------------------------------------------------------------------------
42[deg] N Lat. 600 lb/month.
to
40[deg]10[acute
] N lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
For lingcod south of 40[deg]10[acute] N lat., ACLs for the 2019-20
biennium are lower compared to 2018. Therefore, this rule proposes
reductions to lingcod trip limits for both LEFG and OA. Table 16 below
shows proposed trip limits.
Table 16--Proposed Lingcod Trip Limits South of 40[deg]10[acute] N Lat.
--------------------------------------------------------------------------------------------------------------------------------------------------------
--------------------------------------------------------------------------------------------------------------------------------------------------------
Sector Area Jan-Feb Mar-Apr May-Jun Jul-Aug Sept-Oct Nov-Dec
--------------------------------------------------------------------------------------------------------------------------------------------------------
Limited entry................ 200 lb/2 months. CLOSED.......... 800 lb/2 months. 1,200 lb/2 months 600 lb/........ 300 lb/
month.......... month.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Open Access.................. 300 lb/month.... CLOSED.......... 300 lb/month.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Shortspine and Longspine Rockfish Trip Limits
Retention of shortspine and longspine thornyheads is currently
prohibited year-round for the OA sector north of 34[deg]27[acute] N
lat. This proposed rule would provide a 50 lb (23 kg) per month trip
limit for shortspine and longspine thornyheads north of
40[deg]10[acute] N lat. only. Retention would continue to be prohibited
for OA from 40[deg]10[acute] N lat. to 34[deg]27[acute] N lat. The
Council recommended and NMFS is proposing this trip limit based on an
industry recommendation to allow retention of incidental catches. The
current retention prohibition is likely a holdover from when there were
separate LEFG and OA allocations of thornyheads under the nontrawl
allocation. OA attainment of longspine and shortspine thornyheads north
of 34[deg]27[acute] N latitude would be expected to remain low under
this proposed rule, as they continue to be an incidental catch rather
than a targeted stock.
Primary Sablefish Tier Limits
Some limited entry fixed gear permits are endorsed to receive
annual sablefish quota, or tier limits. Vessels registered
[[Page 47429]]
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
2019, Tier 1 at 47,637 lb (21,608 kg), Tier 2 at 21,653 lb (9,822 kg),
and Tier 3 at 12,373 lb (5,612 kg). In 2020 and beyond, the following
annual limits are in effect: Tier 1 at 48,642 lb (22,064 kg), Tier 2 at
22,110 lb (10,029 kg), and Tier 3 at 12,634 lb (5,731 kg).
H. Recreational Fisheries
This section describes the recreational fisheries management
measures proposed for 2019-20. The Council primarily recommends depth
restrictions and groundfish conservation areas (GCAs) to constrain
catch within the recreational harvest guidelines for each stock. Most
of the changes to recreational management measures are modifications to
existing measures.
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 align the lingcod season in Marine Area 4 with
the recreational groundfish season and the lingcod season in Marine
Areas 1-3. This adjustment would allow for an additional month of
fishing in Marine Area 4 compared to 2018. Additionally, the proposed
rule would allow retention of yellowtail and widow rockfish seaward of
20 fm (37 m) in July and August in Marine Areas 3 and 4. The aggregate
groundfish bag limits off Washington would continue to be nine fish in
all areas. However, the sub-bag limit for canary rockfish, previously 2
fish in all marine areas, would be removed, and the cabezon sub-bag
limit would be changed from two fish per day to one fish for all marine
areas. Additionally, this rule proposes removing the 18-in (45.7-cm)
minimum size limit for cabezon in Marine Area 4. The Council
recommended these changes, which allow more access to target stocks
with fewer restrictions, supported by the proposed increases to the
yelloweye rockfish ACL described in Section C of this rule.
Consistent with the 2017-18 biennium, the Council proposed
continuing 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, the South Coast Recreational YRCA, and the Westport
Offshore YRCA. Coordinates for YRCAs are defined at Sec. 660.70.
Oregon
The Council proposed that Oregon recreational fisheries in 2019-20
would operate under the same season structures and GCAs as provided for
2017-18. This rule also proposes to allow all-depth fishing in April,
May, and September. The Council's proposed expansions to fishing-depth
access during these months is supported by the proposed increased
yelloweye rockfish ACL, described in section II (Harvest
Specifications) C, entitled, ``Proposed ACLs for 2019 and 2020,'' of
this preamble. The Council proposed maintaining the 2017-18 aggregate
bag limits and size limits in Oregon recreational fisheries. 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).
California
The Council manages recreational fisheries off of 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 17 shows the proposed season structure and depth limits by
management area for 2019 and 2020.
[GRAPHIC] [TIFF OMITTED] TP19SE18.000
The Council recommended that size, bag, and sub-bag limits would
remain the same as for 2018 for all stocks except for lingcod. To keep
within allowable limits, the lingcod bag limit would be split into
separate limits for north (42[deg] N lat. (California/Oregon border) to
40[deg]10' N lat. (Northern Management Area)) and south (40[deg]10' N
lat. to the U.S. border with Mexico (Mendocino Management Area, San
Francisco Management Area, Central Management Area, and Southern
Management Area)). The Council proposed maintaining the limit in the
north area at 2 lingcod per day, but recommended reducing the limit in
the south area to 1 lingcod per day (down from 2 in 2018).
Additionally, this rule proposes to allow year-round retention of
California scorpionfish in all management areas, which is supported by
the proposed increase in the ACL for this stock in 2019-20 described in
section II (Harvest Specifications), C, entitled ``Proposed ACLs for
2019 and 2020,'' in this preamble.
[[Page 47430]]
I. Salmon Bycatch Mitigation Measures
In December 2017, NMFS completed an Endangered Species Act (ESA)
consultation on the continued implementation of the PCGFMP and
published a Biological Opinion (available at https://www.pcouncil.org).
As part of its proposed action for the consultation, the Council
estimated Chinook and coho catch in the whiting and non-whiting
groundfish fisheries. The Council estimated that the whiting sector
(including tribal and non-tribal vessels in the mothership, catcher/
processor (C/P), and Shoreside whiting fleets) would take 11,000
Chinook salmon and 474 coho salmon, and the non-whiting sector
(including tribal and non-tribal vessels in the Shoreside trawl, fixed
gear, and recreational fleets) would take 5,500 Chinook salmon and 560
coho salmon.
Additionally, the Council included in its proposed action a reserve
amount of Chinook, 3,500 fish, in the event that bycatch increases
unexpectedly. The reserve is a safeguard against catch exceeding the
total Chinook take estimate, which is an immediate trigger for
reinitiation under section 7 of the ESA. Either the whiting or non-
whiting sector, or both sectors, may access the reserve in a given
year, but the reserve is limited to 3,500 Chinook total. Access to the
reserve is not guaranteed for either sector. Accessing the reserve in
three out of any five consecutive years will also trigger reinitiation
of the ESA consultation.
The incidental take statement (ITS) includes six reasonable and
prudent measures (RPMs) that require the Council and NMFS to take
certain actions to minimize take of endangered and threatened Chinook
and coho salmon in Pacific Coast groundfish fisheries. These RPMs are
non-discretionary, and were developed based on the Biological Opinion's
analysis of the Pacific Coast groundfish fishery's interactions with
salmon. The ITS provides terms and conditions (T&C) under each RPM that
are also non-discretionary, and are required to implement each specific
RPM. Actions performed in compliance with the terms and conditions of
the ITS are not considered to be prohibited taking under the ESA.
The Biological Opinion required that specific T&Cs from the ITS
must be considered within the 2019-20 biennial harvest specifications
and management measures process. These include: (1) Review existing
mechanisms in the PCGFMP and regulations for avoiding and reducing
salmon bycatch to determine if these measures are adequate to allow for
timely inseason management to keep the sectors from exceeding their
bycatch guidelines (T&C 2.a); (2) develop and implement initial
regulations governing the reserve of 3,500 Chinook salmon (T&C 3.a);
and (3) develop automatic closure mechanisms if sectors exceed their
bycatch guideline and/or the reserve (T&C 3.c).
At its March 2018 meeting, the Council's Groundfish Management Team
(GMT) reviewed current monitoring provisions in the PCGFMP, existing
mitigation measures, and historical industry bycatch avoidance tactics
(see Section C.2 of Appendix C of the Analysis). Additionally, the GMT
investigated salmon bycatch data by area, depth, and time for the
whiting and non-whiting midwater trawl sectors to determine if depth
restrictions would be effective for reducing salmon bycatch (see
Section C.3 of Appendix C of the Analysis). As a result of that review,
the Council recommended modifications to existing depth-based
management tools for salmon bycatch mitigation and the creation of new
depth-based management tools to meet T&C 2.a. The Council proposed: (1)
Eliminating the Ocean Salmon Conservation Zone (OSCZ); (2) adding a new
bycatch reduction area (BRA) at the 200 fm (366 m) depth contour for
vessels using midwater trawl gear; (3) prohibiting the use of midwater
trawls and require the use of selective flatfish trawls for any bottom
trawl vessels in the Columbia River Salmon Conservation Zone (CRSCZ)
and the Klamath River Salmon Conservation Zone (KRSCZ); and (4)
implementing automatic closure mechanisms for the Chinook salmon
bycatch guidelines and reserve. The Council and NMFS will continue to
implement other terms and conditions in future rulemakings.
The proposed salmon bycatch mitigation measures would protect ESA-
listed salmon species, and help maintain bycatch below the bycatch
guideline limits described in the proposed action of the Biological
Opinion. Three of the four proposed measures would benefit salmon by
managing bycatch in the groundfish fisheries. The Council proposed
removing the OSCZ because the Analysis suggested that this existing
provision is ineffective for reducing salmon bycatch.
Ocean Salmon Conservation Zone
The OSCZ consists of all waters shoreward of a boundary line
approximating the 100 fm (183 m) depth contour. When NMFS projects that
the Pacific whiting fishery (tribal and non-tribal) may take in excess
of 11,000 Chinook salmon within a calendar year, NMFS implements a
coastwide closure in the OSCZ for all sectors (Pacific whiting IFQ
fishery, the catcher/processor (C/P) sector, and the mothership sector)
through automatic action. The OSCZ was first implemented as an
emergency rule, effective from August 26, 2005, to February 27, 2006
(70 FR 51682; August 31, 2005) as a means to reduce Chinook salmon
bycatch rates in nearshore areas. NMFS later permanently added the OSCZ
as mechanism to limit Chinook salmon interactions in the whiting
fishery during periods of high bycatch (71 FR 78657; December 29,
2006). NMFS has used this depth-based management tool only once since
implementation. On October 20, 2014, NMFS closed the OSCZ to Pacific
whiting vessels after determining the Pacific whiting fishery took over
11,000 Chinook salmon.
The GMT concluded through its review that the OSCZ provision is not
an effective tool for salmon bycatch mitigation. Catch data from 2004
to 2017 demonstrates that, even in high bycatch years, Chinook salmon
catch in the Pacific whiting fishery is not likely to reach the 11,000
fish threshold until the fall, around October. The C/P sector and the
mothership sector have not fished in the depths within the OSCZ after
October since 2011, and the Pacific whiting IFQ fishery has had minimal
activity within the depths of the OCSZ after the fall (see section
C.1.4 of Appendix C of the Analysis). Therefore, by the time the OSCZ
would be triggered by Chinook bycatch in the groundfish fishery, none
of the sectors would be fishing in the area that would be closed. For
these reasons, NMFS proposes to remove the OCSZ provision from the
regulations. Because this provision has limited utility as a bycatch
management tool, NMFS does not expect any discernable effects from
removing this provision from the regulations.
Bycatch Reduction Areas (BRAs)
BRAs are depth-based management provisions used to close waters
shallower than a specified depth contour to fishing in order to
minimize impacts to groundfish or any prohibited or protected species,
such as salmon. Under current regulations, NMFS, in consultation with
the Council and through the routine management process, can implement
BRAs to close areas shoreward of the 75-, 100-, and 150-fm (137-, 183-,
and 274-m) depth contours for a specific sector (i.e., C/P, mothership,
whiting IFQ, and Shoreside IFQ Program non-whiting midwater).
[[Page 47431]]
BRAs are also available through automatic action if a whiting sector is
projected to reach or exceed a sector-specific groundfish allocation
prior to attaining the whiting allocation. However, the 75-, 100-, and
150-fm (137-, 183-, and 274-m) BRAs are not currently available for
salmon bycatch mitigation for any of the sectors and are not proposed
to be modified through this action.
The Council recommended adding the 200-fm (366-m) depth contour as
a BRA available for implementation through routine inseason action to
mitigate salmon bycatch in any of the groundfish midwater trawl
sectors. The groundfish midwater trawl sectors subject to this area
closure would be the Pacific whiting IFQ fishery, the C/P sector, and
the mothership sector, as well as the non-whiting midwater trawl
sector, which primarily targets widow rockfish and yellowtail rockfish.
If the Council and NMFS implemented the 200-fm (366-m) BRA during a
fishing season, vessels using midwater trawl gear to target either
whiting or non-whiting groundfish would be excluded from waters
shoreward of the 200-fm (366-m) depth contour, but would still be
allowed to fish in waters seaward of 200-fm (366-m). This action would
only apply to non-tribal midwater trawl vessels. NMFS expects that the
Tribes would implement area management measures to mitigate salmon
bycatch, if necessary.
The Council and NMFS monitor the salmon bycatch rates of the fleet
inseason. If any sector's bycatch rates exceed those considered in the
Biological Opinion, the Council and NMFS could take inseason action to
implement the BRA for any of the midwater trawl sectors. The effects of
this proposed action would depend on these sectors' ability to fish in
areas deeper than 200 fm (366 m). Section C.1.4 of Appendix C of the
Analysis contains a description of the recent catch data by depth. The
shoreside whiting trawl sector, and especially the non-whiting midwater
trawl sector, would likely have limited or no ability to fish seaward
of 200 fm (366 m) due to horsepower restrictions and because the catch
targets (canary rockfish, widow rockfish, yellowtail rockfish) are
primarily found in shallower depths. The sectors that would be unable
to effectively operate if the proposed BRA were put into place would
experience negative economic effects from this action. The level of
economic impacts would depend on when the BRA was implemented. The non-
whiting midwater trawl fishery typically lands a significant portion of
its catch later in the year. Thus, if NMFS were to implement a BRA
after October, a prohibition on fishing shoreward of 200 fm (366 m)
could significantly reduce this fleet's landings of canary, yellowtail,
and widow rockfish. As discussed in Section 4.3.1.1 of the Analysis, on
average, the non-whiting midwater trawl fleet lands 25.8 percent of its
target stocks from October to December.
The at-sea sectors have historically been able to fish seaward of
200 fm (366 m), but in limited capacity. The MS sector's capacity to
fish seaward of 200 fm (366 m) is particularly limited. Additionally,
data from the C/P and MS sector from 2011 to 2017 has shown higher
amounts of incidental catch of spiny dogfish, yellowtail rockfish, and
widow rockfish seaward of 200 fm (366 m), compared to shoreward of 200
fm (Section C.1.4 of Appendix C of the Analysis). Therefore, if NMFS
implements the 200-fm (366-m) BRA and sectors choose to fish seaward of
200 fm (366 m) due to salmon bycatch concerns, there could be increased
incidental catch of these stocks.
Incidental catch of widow rockfish by the at-sea sector is managed
under an allocation, while catch of yellowtail rockfish is managed
under a set-aside for the sector. Allocations are managed more closely
than set-asides. If an allocation is exceeded, the fishery is closed.
Set-asides are generally managed on an annual basis unless there is a
risk of overall catch exceeding an ACL for the stock, unforeseen
impacts on another fishery, or conservation concerns, in which case
inseason action may be taken. The at-sea sector's catch of both of
these stocks has been at or below allowable amounts in recent years.
For yellowtail rockfish, the overall attainment of the ACL was around
50 percent, so even if at-sea catch increased, NMFS does not expect the
risk of exceeding the ACL to change. Catch of spiny dogfish is managed
under an HG for the entire Pacific Coast groundfish fishery, which
ensures catch will remain below the ACL for this stock.
This proposed action, if approved, would use the existing
regulations for inseason actions, which allow a single meeting process.
If the Council and NMFS determine that any of the midwater trawl
sectors is encountering Chinook salmon at a bycatch rate above that
analyzed in the Biological Opinion, NMFS could issue a single Federal
Register notice to implement the BRA, provided that waiver of notice
and comment meet the requirements of the Administrative Procedure Act.
Columbia River Salmon Conservation Zone and the Klamath River Salmon
Conservation Zone
This proposed action would also close the CRSCZ and the KRSCZ to
all midwater trawling and to bottom trawling, unless vessels are using
a selective flatfish trawl (SFFT). This action is a term and condition
of the Biological Opinion. Under current regulations, vessels using
midwater trawl gear in the Pacific whiting primary season are
prohibited from fishing in the CRSCZ and the KRSCZ. This proposed
action would extend the area prohibition to vessels using midwater
trawl gear to target rockfish, including widow rockfish and yellowtail
rockfish, a reemerging fishery following the rebuilding of widow
rockfish in 2012.
Additionally, this proposed action would maintain protection for
these areas that is currently included under a blanket requirement that
groundfish trawl vessels use SFFT gear shoreward of the trawl RCA north
of 40[deg]10' N lat. Both the CRSCZ and KRSCZ are located inside this
area. NMFS proposed removing this blanket requirement in a separate
proposed rule. This proposed action would reestablish the SFFT
requirement inside the CRSCZ and KRSCZ.
Bycatch Guideline and Reserve Management
This proposed action would create a provision in the regulations to
give NMFS automatic authority to close either or both of the whiting
and non-whiting sector fisheries if: (1) Either sector catches its
guideline limit and the reserve amount; or (2) either sector reaches
its guideline limit when the other sector has already taken the reserve
amount. The closure would be effective until the end of the fishing
year on December 31. This proposed measure is a term and condition of
the Biological Opinion. However, the Council and NMFS intend to use
other available tools, including area management tools, to help manage
salmon bycatch prior to guideline limits being taken, with the result
of sectors being closed for the remainder of the fishing year.
The proposed action organizes the various sectors of the Pacific
Coast groundfish fishery into one of two groupings: The whiting sector
and the non-whiting sector. The whiting sector includes the tribal and
non-tribal Pacific whiting IFQ fishery, the C/P sector, and the
mothership sector. The non-whiting sector includes the tribal and non-
tribal Shoreside IFQ Program, the LEFG fishery, the OA fishery, and the
recreational fisheries off of Washington,
[[Page 47432]]
Oregon, and California. The proposed action includes only select
recreational fisheries that are not accounted for in pre-season salmon
modeling. The recreational fisheries not accounted for in preseason
salmon modeling are those occurring outside of the open salmon seasons
and the Oregon longleader fishery. Any Chinook salmon bycatch in these
fisheries must be attributed to the non-whiting threshold, and these
fisheries are subject to potential closures. Chinook salmon bycatch
from each fishery accrues to the larger sector (i.e., whiting or non-
whiting) level. As described in the Biological Opinion, access to the
reserve for additional Chinook salmon bycatch above the sector's
guideline limit is not guaranteed. However, if one sector surpasses its
guideline limit, it may be allowed to continue fishing, with additional
salmon bycatch accounted for within the reserve. Under such a scenario,
if the sector's bycatch reached the reserve limit, all fisheries within
that sector would be subject to an automatic closure. If one sector is
allowed to access the reserve in a given calendar year, then the other
sector, upon reaching its guideline limit, would be subject to an
automatic closure rather than potentially being able to access the
reserve.
Under the existing regulations for automatic actions at Sec.
660.60(d), a closure notice would be published in the Federal Register
and be effective immediately for all fisheries within either or both of
the whiting or non-whiting sectors. NMFS waives notice and comment
under the Administrative Procedure Act if good cause exists. Section
C.1.4 of Appendix C of the Analysis describes the effects of this
proposed action on the whiting and non-whiting sectors under different
scenarios, based on potential closures lasting from either October or
December through the remainder of the fishing year. Under any of the
closure scenarios, the effect on groundfish would be reduced landings
and underattainment of the ACL for target stocks. The economic effects
of this action are greatest under an October closure scenario, and are
least under a December closure scenario.
The Analysis discusses that both the bottom trawl and non-whiting
midwater trawl sectors typically have high catch after October. Section
4.3.1.1 estimates that an October closure would have the greatest
effect on the C/P fleet because, on average, this fleet catches 45
percent of its whiting catch between October and the end of the year.
Under the December closure scenario, the average percentage of target
catch that could potentially be left unharvested ranges from 0.5
percent for the Shoreside whiting fleet to 13 percent for the
nonwhiting midwater trawl fleet. Overall, Section C.4 of Appendix C of
the Analysis estimates that a closure starting in October could have an
economic impact of $138.6 million in income and 2,083 jobs for the
Pacific Coast groundfish fishery as a whole, assuming no fishery effort
substitutions to offset losses. For the low impact (December only
closure) scenario, the Analysis estimates the impact to be losses of
$24.6 million in income and 349 jobs.
Whether or not there will be an economic impact of a closure
depends upon the likelihood that a closure would occur. Since 2002,
when the West Coast Groundfish Observer Program (WCGOP) first began
monitoring the groundfish fishery, the whiting sector (including the
at-sea, shorebased, and tribal components) has taken more than 11,000
Chinook in two years, in 2005 and in 2014. In the non-whiting sector,
the bottom trawl fleet takes the majority of the salmon bycatch. Since
2002, the bottom trawl fleet has taken more than 5,500 Chinook twice,
in 2002 and 2003. Overall, over the last 15 years, there has never been
a situation where both sectors exceeded their guideline levels at the
same time. Therefore, NMFS believes that it is unlikely that a closure
would be triggered. However, the closure mechanisms are a term and
condition of the Biological Opinion and are, therefore, included in
this proposed rule. Such a mechanism would serve to limit impact on
listed salmon in extraordinary circumstances.
J. Modifications to Depth Restrictions Within the Western CCA
This proposed action would modify the allowed fishing depths from
20-fm (37-m) to 40-fm (73-m) for the commercial fixed gear fishery and
the recreational fishery inside the Western Cowcod Conservation Area
(CCA). This action would also add new waypoints approximating the 30-fm
(55-m) and 40-fm (73-m) depth contours around Santa Barbara Island, San
Nicolas Island, Tanner Bank, and Cortes Bank, because waypoints
approximating these contours do not exist at these depths currently.
Fisheries are allowed to operate in areas shallower than the depth
limit. This proposed action is intended to allow additional
opportunities for commercial fixed gear and recreational vessels to
target healthy stocks (nearshore rockfish, shelf rockfish, cabezon,
kelp greenling, California scorpionfish, and lingcod), while still
closing the depths where the overall density of cowcod is the greatest
to provide protections as the stock continues to rebuild.
The Council originally established two CCAs (Western and Eastern)
in 2001 as area closures to promote cowcod rebuilding. These area
closures prohibited fishing in the main portion of cowcod's depth range
(overall distribution 22 to 270-fm (40 to 494-m), with the highest
density from 100 to 130-fm (183 to 238-m)) to reduce encounters and
mortality to allow the stock to rebuild more quickly. The Western CCA
encompasses 5,126-mi\2\ (13,276-km\2\) and is located in the Southern
California Bight south of Point Conception. The CCA is also expected to
provide protections for bronzespotted rockfish, a stock with similar
life history characteristics, habitat associations, and vulnerability
to fishing as cowcod. Commercial landings of bronzespotted dropped in
the late 1980s and have remained at low levels from 1990 to present.
Under the current regulations, 40.4-mi\2\ (104.6 km\2\) (or less
than 1 percent of the entire CCA) is open to fishing due to the 20-fm
(37-m) depth restriction. By increasing the depth to a 40-fm (73-m)
depth restriction, this proposed rule would increase the fishable area
to 150.4- mi\2\ (389.5-km\2\).
In the 2009-10 biennial specifications and management measures, the
Council recommended modifying the recreational depth restrictions
inside the CCA to 30-fm (55-m). NMFS disapproved this recommendation in
the final rule (76 FR 27508; May 11, 2011), because there was limited
information on the impacts of the proposed action on cowcod, especially
juvenile cowcod, which could delay rebuilding. NMFS also indicated
that, because the ACL for cowcod was low (4 mt at that time), any
measures that potentially increased cowcod mortality required better
information on potential biological and economic effects. At the time
of NMFS' disapproval, cowcod was at 4.5 percent of unfished biomass
with a projected time to rebuild of 2071.
Since the 2009-10 disapproval, the NWFSC conducted a new stock
assessment for cowcod (assessed in 2013). The 2013 assessment concluded
that the stock is rebuilding much more quickly than anticipated under
its rebuilding plan. Cowcod is expected to be rebuilt by 2020, assuming
full removal of the ACL, which is 48 years ahead of the target end date
for the rebuilding plan. Over the past several years, cowcod harvest
has consistently been far below the ACL (see Section C.6 of Appendix C
of the Analysis). As
[[Page 47433]]
discussed in section III (Management Measures), C, entitled ``Biennial
Fishery Allocations,'' of this preamble, NMFS is proposing to set the
cowcod ACT at 6 mt for 2019-20.
The 2013 cowcod assessment explored ecosystem interactions and
updated habitat preferences of juvenile cowcod based on research
published since the previous full assessment in 2007. The stock
assessment identified young of the year fish as being distributed
between 52 and 277-m (28-151-fm), with juveniles found slightly deeper.
NMFS survey data and recent catch data from observed trips inside the
Western CCA encountered no cowcod (juvenile or adult) within the
proposed depth openings (see Section C.6 of Appendix C of the
Analysis). Overall, the proposed measure is not expected to result in
increased cowcod encounters, because the highest densities of cowcod
are found outside of the depths in which this measure would allow
commercial fixed gear and recreational fishing. Additionally, the
proposed measure is not expected to increase mortality for
bronzespotted rockfish, because this stock is found between 41-fm (75-
m) and 205-fm (375-m), which is outside the depth range of the proposed
action.
The Council recommended this measure because the additional data on
habitat usage from the 2013 stock assessment, the improved cowcod stock
trajectory, and the higher ACT for cowcod demonstrate that there would
be no adverse impacts expected for cowcod from this action. The
expected benefits of this action for the commercial and recreational
fleets are described separately below.
Commercial
This proposed action would allow greater access to valuable and
underattained stocks in this remote area. Recent commercial fixed gear
fishing effort has been very low within the Western CCA due to limited
opportunities within the current depth restrictions. The proposed depth
changes within the CCA would allow greater access to deeper stocks and
would create an economic incentive for vessels to make trips to the
area. NMFS expects that a modest increase in the number of fixed gear
vessels fishing in this area may occur as a result of this proposed
action; however the magnitude of increase is difficult to quantify. A
redistribution of depth of catch is also expected as a result of the
increased depths available for fishing. The effects on groundfish of
any increase in effort would be limited through the existing 2-month
trip limits delineated in Table 2 (South) to part 660.330.
Recreational
This proposed action would allow recreational fishing within the
Western CCA out to 40 fathoms (73 m). NMFS expects this measure would
increase the catch of target stocks, including shelf rockfish,
bocaccio, deeper nearshore rockfish, and lingcod. The proposed action
would also be expected to reduce pressure on shallower nearshore
rockfish stocks by allowing access to currently inaccessible desirable
nearshore (i.e., copper rockfish) and shelf rockfish (i.e., vermilion
rockfish) found in deeper waters.
NMFS expects that this action would result in an increase in the
number of angler trips, and an increase in the amount of recreational
catch, and result in a redistribution of depth of catch. Allowing
access to deeper depths inside the Western CCA is expected to increase
the number of groundfish trips between 10 percent and 20 percent,
particularly out of Ventura and Los Angeles, given the proximity of
these ports to the Western CCA (see Section C.7 of Appendix C of the
Analysis). This would provide additional revenues to charter boat crews
in the form of fish processing and tips.
K. Modification of Lingcod and Sablefish Discard Mortality Rates
This rule proposes to modify the discard mortality rates (DMRs) for
lingcod and sablefish used to debit IFQ accounts in the Shorebased IFQ
Program. Currently, NMFS debits IFQ accounts for 100 percent of all
catch of these stocks, regardless of survival after discarding. The
Council recommended implementing lower discard mortality rates for
lingcod and sablefish to match those endorsed by the SSC and used for
year-end groundfish catch accounting. For many other stocks, the best
scientific information available does not indicate discard survival
rates high enough to warrant consideration of a survival credit. The
DMRs in Table 18 reflect the best scientific information available.
Table 18--Proposed Discard Mortality Rates for Lingcod and Sablefish
------------------------------------------------------------------------
Proposed DMR
Stock Gear (percent)
------------------------------------------------------------------------
Lingcod........................... Bottom trawl........ 50
Fixed gear \a\...... 7
Sablefish......................... Bottom trawl........ 50
Fixed gear \a\...... 20
------------------------------------------------------------------------
\a\ Applies to both pot and hook and line gear.
By providing IFQ participants with discard survival credits for
lingcod and sablefish, this action better meets some of the objectives
of the IFQ program, such as increased attainments of and increased
value of IFQ stocks, such as Dover sole and thornyheads. In addition,
this action aligns DMRs with those used in year-end catch accounting,
which creates consistency in mortality estimates. This proposed action
would allow modest increases in attainment of co-occurring target
stocks, and increase marketability and value of retained catch by
eliminating the need to retain small fish that are not economically
marketable or desirable. Landings and mortality would be expected to
increase proportionally by the amount of QP savings/gains the credit
would provide, which for sablefish could be a gain of one-half the
bottom trawl discards (9-21 mt per year) and four-fifths the fixed gear
discards (11-20 mt per year), which could be converted into additional
landings. Therefore, the resulting gains in landings of sablefish could
be an extra 5-11 mt for bottom trawl and 9-16 mt for fixed gear, which
would only be about a 1 percent increase in total coastwide IFQ
mortality of this stock (see Section C.5 of Appendix C of the
Analysis).
As described in Section C.5 of Appendix C of the Analysis, overall,
this proposed action would not be expected to result in substantial
changes to discarding behavior because there are operational costs for
discarding in terms of labor time for sorting catch, extra fishing time
necessary to replace the
[[Page 47434]]
discarded fish, as well as the potential risk that further fishing will
not result in catching larger fish. However, the resulting ``savings''
of trawl sablefish, due to a decreased deduction for discarded fish,
could possibly increase landings of co-occurring, underattained stocks,
such as Dover sole, shortspine thornyheads, and longspine thornyheads
(see Section C.5 of Appendix C of the Analysis). Although this measure
could increase attainment, IFQ participants' total fishing mortality
would continue to be managed to individual and sector allocations, and
catch would be constrained by the total ACL for each stock.
L. Removal of IFQ Daily Vessel Limits
Under the Shorebased IFQ Program, a quota share (QS) permit
authorizes a person or group to own QS. A QS account is an account that
contains QS allocations registered to the QS permit for IFQ and
individual bycatch quota (IBQ) stocks. At the beginning of each
calendar year, NMFS issues quota pounds (QPs) to each QS account based
on the IFQ or IBQ sector allocation. For QPs to cover catch (landings
and discards) by a vessel in the shorebased IFQ program, the QS permit
owner must transfer QPs from the QS account to a vessel account. Vessel
limits in vessel accounts restrict the amount of QPs that any vessel
can catch or hold. NMFS calculates annual QP vessel limits, which are a
set percentage of the total IFQ sector allocation based on formulas set
through Amendment 20 to the PCGFMP. The annual vessel QP limit
restricts the amount of used and unused QP in a vessel account during a
fishing year.
NMFS also sets daily vessel limits for overfished stocks, which cap
the amount of overfished stock QPs any vessel account can have
available in their account on a given day. The Council and NMFS
established daily vessel limits to prevent a person from acquiring
additional QP from others before those QP are needed. IFQ sector
allocations of some overfished stocks are low, which creates a strong
incentive for hoarding of QP for these stocks to cover unexpected high
catch events. This daily limit keeps QP of overfished stocks on the
market and available for trading. The daily limits are set equal to the
control limits for each stock, which limit the amount of QS and IBQ
that a person, individually or collectively, may own or control.
Because daily limits are set at the level of the QS control limits,
they have no effect on those who only use QP from their own QS account.
Amendment 20 to the PCGFMP intended for daily limits to apply for
overfished stocks. This means that when stocks are declared rebuilt,
the daily limit for that stock must be removed through rulemaking. In
the 2017-18 biennium, bocaccio (south), darkblotched rockfish, and
Pacific ocean perch were declared rebuilt, so this action proposes to
remove the daily limits for these stocks. However, because the daily
vessel limit has been ineffective for keeping catch available for
trading, this rule proposes to eliminate the daily limits for all
stocks. Thus, in addition to bocaccio (south), darkblotched rockfish,
and Pacific ocean perch, this rule also proposed to remove daily
vessels limits for cowcod (south), yelloweye rockfish, and Pacific
halibut.
As explained in in Section C.5 of Appendix C of the Analysis, there
may be strategies to circumvent the daily vessel limit. First, vessel
owners can sign sales contracts in advance, but delay transferring QP
for a stock until a vessel account's unused QP drops below the daily
limit. Second, entities can temporarily acquire trawl permits and use
them to establish a second vessel account in which they can store QP.
There is also evidence that the daily limit is not constraining for
several stocks. Table C-65 in the Analysis indicates that for the
remaining overfished stocks and Pacific halibut, from 2011 through
2017, there has been only one instance of a vessel landing more than
the daily limit. For the recently rebuilt stocks, there has generally
been at least one vessel landing more than the daily limit each year
for Pacific ocean perch, but this has rarely occurred for bocaccio and
darkblotched rockfish since the start of the Shorebased IFQ Program.
Because the daily limits for the remaining overfished stocks and for
Pacific halibut have not been constraining, NMFS expects that
eliminating this provision would not have a measurable effect on the
fishery.
M. Removal of Automatic Authority for Darkblotched Rockfish and Pacific
Ocean Perch Set-Asides for At-Sea Sector
Amendment 21 to the PCGFMP (75 FR 60867; October 1, 2010)
established allocations for darkblotched rockfish and Pacific ocean
perch catch in the at-sea sector (C/P and mothership sectors). At that
time, darkblotched rockfish and Pacific ocean perch were overfished,
and the ACLs and fishery allocations for these stocks were low. NMFS
has authority to take automatic action to close the at-sea sector, if
necessary, to ensure that darkblotched rockfish and Pacific ocean perch
stays below the allocation. In recent years, both of the at-sea sectors
have exceeded their allocations of darkblotched rockfish (the C/P
sector in 2011, and the mothership sector in 2014). The latter resulted
in an emergency Council meeting, and NMFS took emergency action to
reopen the fisheries (79 FR 67095; November 12, 2014). However, because
the overall attainment of the darkblotched rockfish ACL had been low,
the Council recommended and NMFS approved Amendment 21-3 to the PCGFMP
(83 FR 757; January 8, 2018). Amendment 21-3 replaced the at-sea sector
Pacific ocean perch and darkblotched rockfish allocations with sector-
specific set-asides with a reserve for the C/P and mothership sectors.
The allocation for the at-sea sectors is a percentage of the trawl
allocation of each stock.
Set-asides are managed on an annual basis unless there is a risk of
catch exceeding a harvest specification (ACL, ACT, or HG) inseason,
unforeseen impact on another fishery, or conservation concerns, in
which case inseason action may be taken. Amendment 21-3 also included a
reserve, or buffer, for set-asides. The buffer is an amount deducted
from the ACL as part of the process of determining the fishery HG
(which serves as the basis of allocating between trawl and nontrawl
fisheries), and is intended to account for higher than expected
incidental catch. The buffer for darkblotched rockfish and Pacific
ocean perch was established under Amendment 27 to the PCGFMP (82 FR
9634; February 7, 2017). NMFS has the authority to close either at-sea
sector if it is projected to exceed its set-aside value, taking into
account the buffer, for either darkblotched rockfish or Pacific ocean
perch.
Darkblotched rockfish and Pacific ocean perch have both been
declared rebuilt. The proposed 2019-20 ACLs for both stocks are higher,
reflecting the change in stock status. In addition, because of the
change in stock status, there is currently no buffer proposed for 2019-
20. Because of these changes, darkblotched rockfish and Pacific ocean
perch would be managed as de facto allocations for the at-sea sectors.
This proposed rule would remove NMFS's automatic authority to close
either sector if they exceed their set-aside value for these stocks, so
that they are managed like all other at-sea set-asides in the PCGFMP.
The Analysis demonstrates that the expected risk of the at-sea sectors
exceeding their set-aside values for darkblotched rockfish and Pacific
ocean perch is low, due to low overall attainment in the trawl
[[Page 47435]]
sector in recent years. In addition, because this proposed adjustment
would remove the risk of shutting down the fishery after reaching the
set aside, it increases the likelihood that the at-sea sectors could
attain their Pacific whiting allocation (see Section C.4 of Appendix C
of the Analysis).
N. Continuation of Adaptive Management Pass Through
Under the Amendment 20 Trawl Rationalization Program, NMFS reserves
10 percent of the QS for each of the non-whiting stocks (including
halibut individual bycatch quota) each year for an adaptive management
program. While the Council has never used the allocation for this
purpose, conceptually, an adaptive management program could distribute
the reserved QP to fishery participants to address adverse effects of
the Shoreside IFQ program, including impacts to community or processor
stability, conservation concerns, or other effects. NMFS could also
distribute the reserved QPs to facilitate new entrants to participate
in the groundfish fishery. To date, the Council has not recommended
establishing an adaptive management program. Therefore, NMFS has
distributed (passed through) these QP to quota shareholders each
fishing year in proportion to their QS for each stock. This rule
proposes that NMFS will continue to pass through the QP reserved for
the adaptive management program until the Council recommends an
alternative use of adaptive management program QP. This is an
administrative measure that would not affect fishing opportunity and
related catch.
O. Modification of the Incidental Lingcod Retention Ratio in the Salmon
Troll Fishery
This proposed action would adjust the existing incidental retention
ratio for landing lingcod based on the number of Chinook landed in the
ocean salmon troll fishery in the area north of 40[deg] 10' N.
latitude. The purpose of the ratio is to allow salmon trollers to
retain incidentally caught lingcod, but to discourage lingcod
targeting. Currently, participants are allowed to retain 1 lingcod per
15 Chinook salmon plus 1 lingcod per trip, up to a trip limit of 10
lingcod, on a trip where any fishing occurs within the nontrawl RCA.
This limit only applies when lingcod retention is allowed. Vessels
participating in the ocean salmon troll fishery must be equipped with a
vessel monitoring system (VMS) to retain incidentally caught
groundfish. This proposed action would allow retention of 1 lingcod per
5 Chinook salmon plus 1 lingcod per trip, up to a trip limit of 10
lingcod, on a trip where any fishing occurs within the RCA. For 2019-
20, the lingcod fishery is proposed to be open year-round for the open
access groundfish fishery. The Council can adjust the ratio of lingcod
retention per Chinook landed through inseason adjustments, if
necessary.
As Section C.9 of Appendix C of the Analysis notes, this action
would be the first modification of the ratio since it was implemented
in 2009 (74 FR 9874; March 6, 2009). The Council recommended this
measure because there has been an increased rate of lingcod encounters
as Chinook harvest opportunities have declined. This increased
encounter rate has resulted in an increase in regulatory discards of
lingcod. This proposed action would align the lingcod retention limit
with the true lingcod encounter rate in the salmon troll fishery while
continuing to discourage lingcod targeting. Salmon trollers would still
to be subject to the existing overall limit of 10 lingcod per trip and
the existing requirement to have VMS in order to retain any
incidentally caught groundfish. NMFS does not expect this proposed
action will create an incentive for salmon trollers to target lingcod
because these vessels would still be restricted to an overall limit of
10 lingcod per trip.
P. Administrative Actions
NMFS also proposes four minor changes to the regulatory text to
clarify regulatory intent. NMFS proposes to add big skate to the LEFG
and OA fixed gear fisheries trip limit tables, Table 2 North and Table
2 South to Part 660 Subpart E, and Table 3 North and Table 3 South to
Part 660 Subpart F. Big skate is not currently listed in the trip limit
table for either the LEFG or OA fisheries, and as such is unlimited.
Adding it to the trip limit tables would provide clarity on this
existing management measure.
This proposed rule would remove an obsolete reference to halibut
weight provisions at Sec. 660.333(c)(3). The obsolete reference
originally mirrored a provision in California state regulations, but
the California Department of Fish and Wildlife removed this provision
from state regulations in 2004.
This proposed rule would clarify the application of Amendment 21-3
set-aside management of darkblotched rockfish and Pacific ocean perch
for the at-sea sector for both years of the biennium in Tables 1b, 2b,
1d, and 2d to part 660, subpart C.
Finally, this action would remove the WCGOP priority sampling
requirement for canary rockfish and bocaccio, formerly overfished
stocks that were declared rebuilt, as requested by the Council at their
March 2017 meeting. Under this requirement, observers are required to
count and weigh these fish on a docked vessel prior to offloading. This
requirement was implemented to prevent vessels from discarding
overfished stocks for which they may have low QP at port prior to
offload. Under 50 CFR 660.60(c)(1), the Council can modify the list of
stocks subject to this catch monitoring requirement as a routine
management measure. In March 2017, the Council recommended that the
priority sampling requirement be removed for canary rockfish and
bocaccio because these stocks are now rebuilt.
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 state, ``the Secretary will develop tribal
allocations and regulations under this paragraph in consultation with
the affected tribe(s) and, insofar as possible, with tribal
consensus.'' The tribal management measures in this proposed rule have
been developed following these procedures. The 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
[[Page 47436]]
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.
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 ten year projections for routinely adjusted
harvest specifications and management measures. The ten year
projections were produced to evaluate the impacts of the ongoing
implementation of harvest specifications and management measures and to
evaluate the impacts of the routine adjustments that are the main
component of each biennial cycle. Therefore, the EA for the 2019-20
cycle tiers from the 2015-16 EIS and focuses on the harvest
specifications and management measures that were not within the scope
of the ten 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.
An initial regulatory flexibility analysis (IRFA) was prepared for
this action, as required by section 603 of the Regulatory Flexibility
Act (RFA) (5 U.S.C. 603). The IRFA describes the economic impact this
proposed rule, if adopted, would have on small entities. A description
of the action, why it is being considered, and the legal basis for this
action is contained in the SUMMARY section and at the beginning of the
SUPPLEMENTARY INFORMATION section of the preamble. A summary of the
IRFA follows. A copy of the IRFA is available from NMFS (see
ADDRESSES).
When an agency proposes regulations, the RFA requires the agency to
prepare and make available for public comment an IRFA that describes
the impact on small businesses, non-profit enterprises, local
governments, and other small entities. The IRFA is to aid the agency in
considering all reasonable regulatory alternatives that would minimize
the economic impact on affected small entities.
The RFA (5 U.S.C. 601 et seq.) requires government agencies to
assess the effects that regulatory alternatives would have on small
entities, defined as any business/organization independently owned and
operated, not dominant in its field of operation (including its
affiliates). A small harvesting business has combined annual receipts
of $11 million \2\ or less for all affiliated operations worldwide.
---------------------------------------------------------------------------
\2\ On December 29, 2015, the National Marine Fisheries Service
(NMFS) issued a final rule establishing a small business size
standard of $11 million in annual gross receipts for all businesses
primarily engaged in the commercial fishing industry (NAICS 11411)
for Regulatory Flexibility Act (RFA) compliance purposes only (80 FR
81194, December 29, 2015; 50 CFR part 200). The $11 million standard
became effective on July 1, 2016, and after that date it is to be
used in all NMFS rules subject to the RFA. Id. at 81194. This NMFS
rule is to be used in place of the U.S. Small Business
Administration's (SBA) current standards of $20.5 million, $5.5
million, and $7.5 million for the finfish (NAICS 114111), shellfish
(NAICS 114112), and other marine fishing (NAICS 114119) sectors of
the U.S. commercial fishing industry, respectively.
---------------------------------------------------------------------------
A small fish-processing business is one that employs 750 or fewer
persons for all affiliated operations worldwide. NMFS is applying this
standard to catcher/processors (C/Ps) for the purposes of this
rulemaking, because these vessels earn the majority of their revenue
from selling processed fish.
For marinas and charter/party boats, a small business is one that
has annual receipts not in excess of $7.5 million. A wholesale business
servicing the fishing industry is a small business if it employs 100 or
fewer persons on a full-time, part-time, temporary, or other basis, at
all its affiliated operations worldwide.
For the purposes of this rulemaking, a nonprofit organization is
determined to be ``not dominant in its field of operation'' if it is
considered small under one of the following Small Business
Administration (SBA) size standards: environmental, conservation, or
professional organizations are considered small if they have combined
annual receipts of $15 million or less, and other organizations are
considered small if they have combined annual receipts of $7.5 million
or less. The RFA defines small governmental jurisdictions as
governments of cities, counties, towns, townships, villages, school
districts, or special districts with populations of less than 50,000.
Description and estimate of the number of small entities to which the
rule applies, and estimate of economic impacts by entity size and
industry
This proposed rule would regulate businesses that participate in
the groundfish fishery. This rule would directly affect commercial
vessels in the groundfish fisheries, trawl QS holders and Pacific
whiting catch history endorsed permit holders (which include shorebased
whiting processors), tribal vessels, and charterboat vessels.
Additionally, a provision of this proposed rule would regulate
commercial vessels in the salmon troll fleet.
To determine the number of small entities potentially affected by
this rule, NMFS reviewed analyses of fish ticket data and limited entry
permit data, information on charterboat, tribal, and open access
fleets, available cost-earnings data developed by NWFSC, and responses
associated with the permitting process for the Trawl Rationalization
Program where applicants were asked if they considered themselves a
small business based on SBA definitions. This rule would primarily
regulate businesses that harvest groundfish.
Charter Operations
There were an estimated 287 active Commercial Passenger Fishing
Vessels (charter boats) engaged in groundfish fishing in California in
2017. In 2017, an estimated 49 charter boats targeted groundfish in
Oregon. There is no Oregon license or tracking of party fishing (or
``six pack'') vessel businesses that will also be impacted, however in
one week in August 2017, there were 285 boat trips targeting
recreational groundfish in Oregon; this number includes the 49 charter
vessels and is the upper bound of the number of such entities likely to
be impacted in Oregon. Similarly in Washington, the number of party/
charter vessels likely to be impacted by the proposed rule was 182 in
2017. All 705 of these vessels are likely to be impacted by changes in
recreational catch guidelines for groundfish in their respective
states.
Commercial Vessels
Groundfish
Entities that are not registered as trusts, estates, governments,
or non-profits are assumed to earn the majority of their revenue from
commercial fishing. There are 124 QS permit owners, who collectively
received 76.5 percent of the QP issued in 2018. Limited entry
groundfish vessels are required to self-report size across all
affiliated entities; of the business who earn the majority of their
revenue from commercial fishing, one self-reported as large. This
entity owns four groundfish permits and one QS permit. 264 entities
owning 376 permits self-reported as small. The average small entity
owns 1.4 permits, with 30 small entities owning between 3-6 permits
each. Open access groundfish vessel owners are assumed
[[Page 47437]]
to earn the majority of their revenue from fishing and would thus fall
into this Small Business Administration definition. 186 non-limited
entry vessels harvested at least $10,000 worth of groundfish in 2017;
these are likely to be impacted by the proposed rule. This number is
likely an upper bound, as some entities may own more than one vessel.
However, these generally small operations are assumed to be independent
entities; with the top three vessels having coastwide (including non-
groundfish) revenues averaging $585,000. Median revenues were $37,000
per vessel.
In addition to benefits from increasing ACLs in the harvest
specifications, several of the new management measures contained in the
proposed rule are likely to benefit vessels. Clarifications resulting
from the stock complex restructuring and updates to Rockfish
Conservation Area coordinates may streamline management burden for
vessels. IFQ vessels are expected to benefit from the removal of daily
vessel quota pounds, which did not appear to constrain operations, but
which did account for some level of administrative burden for quota
pound account managers. With the elimination of these limits, managers
will have greater flexibility in moving and holding quota pounds for
the remaining overfished species and halibut IBQ. These vessels and
vessel account operators may also benefit somewhat from changes to the
discard mortality rates in the IFQ program. Some of the non-trawl fixed
gear vessels are expected to benefit by the modifications to the
commercial depths inside the Western Cowcod Conservation area in
California.
Salmon Trollers
The proposed rule primarily impacts entities in the groundfish
fishery. However, one new management measure included the proposed rule
will likely benefit vessels primarily involved in the salmon troll
fishery, through a modification in the incidental lingcod retention
ratio in that fishery. This modification reflects the increased rate of
lingcod encounters during declining Chinook salmon harvest seasons.
This modification would allow salmon trollers to retain and sell a
larger number of lingcod caught incidentally when targeting salmon. The
level of activity varies substantially, with trips ranging from 500 to
over 5,500 in a year. The subsector of the fleet expected to benefit
from the proposed rule is much smaller, as historically a small
proportion has elected to land lingcod within the previously allowed
limits. In order to land lingcod, the vessel would have to install VMS,
which (among other factors) likely deters salmon trollers. Thus, this
provision of the proposed rule is likely to impact 3 of 220 vessels
operating in California. In Oregon, between 7 and 85 trollers have
landed lingcod, and in Washington between 10 and 17 trollers have
landed lingcod. The proposed rule would confer a small benefit to these
105 vessels, which landed lingcod on a median of 1-2 trips, with
vessels in the 90th percentile landing lingcod on 5 trips annually.
This small positive benefit is not expected to be a substantial impact.
A substantial number of small entities in the overall salmon troll
fishery are not likely to be impacted by the proposed rule.
QS Owners
Because the harvest specifications process determines the amount of
QP available in the catch share (Shorebased IFQ Program) sector, this
proposed rule will impact QS. Twenty-two non-whiting QS permit owners
are estimated to be primarily engaged in seafood product preparation
and packaging, based on holdings of first receiver permit affiliation
in the non-public West Coast Region permits database. According to the
size standard described above, three of the entities that own three of
these permits are considered small. These small processing entities
were issued 1.7 percent of the non-whiting QP issued in 2018. Some of
these small processing entities also own groundfish permits, which are
required on both catcher vessels and catcher processors, and which
would be regulated by the proposed rule; three small entities primarily
engaged in seafood processing own two groundfish permits. Thirty
groundfish vessel permits are owned by seven entities that are
considered large, as estimated by NMFS using the standard described
above, and as estimated by information regarding ownership affiliation
and self-reported size on groundfish permits and first receiver site
license permits (self-reported using the standard described above). Six
of these seven large processing entities were issued 10.2 percent of
the non-whiting QP issued in 2018 across sixteen QS permits.
Governmental Jurisdictions
According to the public IFQ Account database as of June 19, 2018,
the City of Monterey owns QS of ten stocks. The U.S. Census estimates
the population to be 28,454 as of July 1, 2017, so would be considered
a small governmental jurisdiction by the RFA standard noted above. The
City of Monterey received 0.5 percent of the QP issued for 2018,
according to the public IFQ Account database.
Not-for-Profits
According to the public IFQ Account database, six not-for-profit
organizations own QS in the catch share program and would thus be
impacted by the trawl sector allocation under this proposed rule. Five
of these would be considered small by the definition noted above (with
2016 annual receipts as reported on IRS form 990 of $120-500 thousand
dollars), and one would be considered large (with self-reported fiscal
year 2017 receipts of $1.1 billion). Collectively, the five small not-
for-profit organizations received 7.2 percent of the non-whiting \3\ QP
issued in 2018, and the large not-for-profit organization received 0.5
percent. The large not-for-profit organization also owned four limited
entry trawl permits which would be impacted by the management measures
of the rule.
---------------------------------------------------------------------------
\3\ Whiting is issued annually through a separate rulemaking
process resulting from international treaty negotiations. (See 83 FR
22401 for more information and 2018 allocations.)
---------------------------------------------------------------------------
Small Trusts
Eleven personal or family trusts/estates owned QS permits and would
thus potentially be impacted by the trawl sector allocation under this
proposed rule. All of these are assumed to be smaller than the size
standard noted above. Collectively, these eight small entities received
4.2 percent of the non-whiting QP issued for 2018.
A description of any significant alternatives to the proposed rule that
accomplish the stated objectives of applicable statutes and that
minimize any significant economic impact of the proposed rule on small
entities
In the event of a fishery closure under the Biological Opinion
provisions included in this rule (50 CFR 660.60(d)(1)(v) and (vi) of
this proposed rule), the loss of revenue in groundfish fisheries would
likely have a substantial negative impact on a significant number of
small entities, and an equal impact on all large entities in the
fishery. However, such a closure is not anticipated by NMFS and the
Council, given historic catch levels and the existence of cooperative
management structures with extensive inseason monitoring. Because these
provisions are non-discretionary under the ESA, there are no
significant alternatives to the proposed rule that would minimize
adverse economic impacts on small entities.
The Council considered alternatives to the actions in this proposed
rule that
[[Page 47438]]
would have a lower level of benefits to small entities. The Council did
not consider alternatives that would have greater benefits to small
entities, as these would not have met several primary objectives of the
rule (the prevention of overfishing, the rebuilding of overfished
stocks, and ensuring conservation).
Under the No Action alternative, the default harvest specifications
and associated routine management measures would be implemented using
best scientific information available to establish default harvest
control rules for all groundfish stocks. The Council considered
alternative specifications for California scorpionfish, lingcod north
of 40[deg]10' N lat, and yelloweye rockfish. In each case, the Council
selected the harvest control rule that resulted in the maximum benefits
to both large and small directly regulated entities. Routine management
measures are adjusted according to harvest specifications, which also
impact the new management measures available for implementation.
Regulatory Flexibility Act (RFA) Determination of No Significant Impact
The RFA requires Federal agencies to conduct an analysis of the
impact of the proposed rule on small entities. The proposed rule would
impact a significant number of small entities, but that these impacts
are expected to range from neutral to positive, depending on individual
response to increased harvest guidelines and updated management
measures. Because there are no anticipated compliance costs or other
adverse effects, NMFS concludes (subject to review of any pertinent
public comments) that the rule will not have a substantial adverse
impact on the significant number of directly regulated entities.
List of Subjects in 50 CFR Part 660
Fisheries, Fishing, Reporting and recordkeeping requirements.
Dated: September 4, 2018.
Samuel D. Rauch III,
Deputy Assistant Administrator for Regulatory Programs, National Marine
Fisheries Service.
For the reasons set out in the preamble, 50 CFR part 660 is
proposed to be amended as follows:
PART 660--FISHERIES OFF WEST COAST STATES
0
1. The authority citation for part 660 continues to read as follows:
Authority: 16 U.S.C. 1801 et seq., 16 U.S.C. 773 et seq., and 16
U.S.C. 7001 et seq.
0
2. In Sec. 660.11:
0
a. In the definition of ``Conservation area(s)'', revise paragraph (1);
and
0
b. In the definition of ``Groundfish'':
0
i. Revise paragraphs (6) and (7)(i) introductory text;
0
ii. Redesignate paragraph (7)(i)(B) as (7)(i)(C);
0
iii. Add new paragraph (7)(i)(B); and
0
iv. Revise paragraph (9).
The revisions and additions read as follows:
Sec. 660.11 General definitions.
* * * * *
Conservation Area(s) * * *
(1) Groundfish Conservation Area or GCA means a geographic area
defined by coordinates expressed in degrees latitude and longitude,
wherein fishing by a particular gear type or types may be prohibited.
Regulations at Sec. 660.60(c)(3) describe the various purposes for
which these GCAs may be implemented. Regulations at Sec. 660.70 define
coordinates for these polygonal GCAs: Yelloweye Rockfish Conservation
Areas, Cowcod Conservation Areas, waters encircling the Farallon
Islands, and waters encircling the Cordell Bank. GCAs also include
Bycatch Reduction Areas (BRAs), and Rockfish Conservation Areas or
RCAs, which are areas closed to fishing by particular gear types,
bounded by lines approximating particular depth contours. RCA
boundaries may and do change seasonally according to conservation
needs. Regulations at Sec. Sec. 660.70 through 660.74 define boundary
lines with latitude/longitude coordinates; regulations at Tables 1
(North) and 1 (South) of subpart D, Tables 2 (North) and 2 (South) of
subpart E, and Tables 3 (North) and 3 (South) of subpart F set seasonal
boundaries. Fishing prohibitions associated with GCAs are in addition
to those associated with EFH Conservation Areas.
* * * * *
Groundfish * * *
* * * * *
(6) Roundfish: Cabezon, Scorpaenichthys marmoratus; kelp greenling,
Hexagrammos decagrammus; lingcod, Ophiodon elongatus; Pacific cod,
Gadus macrocephalus; Pacific whiting, Merluccius productus; sablefish,
Anoplopoma fimbria. Species listed below with an area-specific listing
are managed within a complex in that area-specific listing.
(i) Between 46[deg]16' N lat. and the U.S. Canada border
(Washington): Cabezon, S. marmoratus and kelp greenling, H.
decagrammus.
(ii) Between 46[deg]16' N lat. and 42[deg] N lat. (Oregon):
Cabezon, S. marmoratus and kelp greenling, H. decagrammus.
(7) * * *
(i) Nearshore rockfish includes black rockfish, Sebastes melanops
(off Washington) and the following nearshore rockfish species managed
in ``minor rockfish'' complexes:
* * * * *
(B) Between 46[deg]16' N lat. and 42[deg] N lat. (Oregon): black
rockfish, S. melanops, blue rockfish, S. mystinus, deacon rockfish, S.
diaconus.
* * * * *
(9) ``Other Fish'': kelp greenling (Hexagrammos decagrammus) off
California and leopard shark (Trakis semifasciata).
* * * * *
0
3. Amend Sec. 660.40 as follows:
0
a. Remove paragraphs (a), (c), and (d);
0
b. Redesignate paragraph (b) as paragraph (a), and paragraph (e) as
paragraph (b); and
0
c. Revise newly redesignated paragraph (b).
The revision reads as follows:
Sec. 660.40 Overfished species rebuilding plans.
* * * * *
(b) Yelloweye rockfish. Yelloweye rockfish was declared overfished
in 2002. The target year for rebuilding the yelloweye rockfish stock to
BMSY is 2029. The harvest control rule to be used to rebuild
the yelloweye rockfish stock is an annual SPR harvest rate of 65.0
percent.
0
4. In Sec. 660.50, revise paragraphs (f)(2)(ii) and (f)(6) and add
paragraph (h) to read as follows:
Sec. 660.50 Pacific Coast treaty Indian fisheries.
* * * * *
(f) * * *
(2) * * *
(ii) The Tribal allocation is 561 mt in 2019 and 572 mt in 2020 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 1.5 percent for estimated discard mortality.
* * * * *
(6) Petrale sole. For petrale sole, treaty fishing vessels are
restricted to a fleetwide harvest target of 290 mt each year.
* * * * *
(h) Salmon bycatch. This fishery may be closed through automatic
action at 660.60(d)(1)(v) and (d)(1)(vi).
0
5. In Sec. 660.55, revise paragraphs (c)(1)(i)(A) and (B) to read as
follows:
[[Page 47439]]
Sec. 660.55 Allocations.
* * * * *
(c) * * *
(1) * * *
(i) * * *
(A) Darkblotched rockfish. Distribute 9 percent or 25 mt, whichever
is greater, of the total trawl allocation of darkblotched rockfish to
the Pacific whiting fishery (MS sector, C/P sector, and Shorebased IFQ
sectors). The distribution of darkblotched rockfish to each sector will
be done pro rata relative to the sector's allocation of the commercial
harvest guideline for Pacific whiting. Darkblotched rockfish
distributed to the MS sector and C/P sector are managed as set-asides
at Table 1d and Table 2d, subpart C. The allocation of darkblotched
rockfish to the Pacific whiting IFQ fishery contributes to the
Shorebased IFQ allocation. After deducting allocations for the Pacific
whiting fishery, the remaining trawl allocation is allocated to the
Shorebased IFQ Program.
(B) Pacific Ocean Perch (POP). Distribute 17 percent or 30 mt,
whichever is greater, of the total trawl allocation of POP to the
Pacific whiting fishery (MS sector, C/P sector, and Shorebased IFQ
sector). The distribution of POP to each sector will be done pro rata
relative to the sector's allocation of the commercial harvest guideline
for Pacific whiting. POP distributed to the MS sector and C/P sector
are managed as set-asides at Table 1d and Table 2d, subpart C. The
allocation of POP to the Pacific whiting IFQ fishery contributes to the
Shorebased IFQ allocation. After deducting allocations for the Pacific
whiting fishery, the remaining trawl allocation is allocated to the
Shorebased IFQ Program.
* * * * *
0
6. Amend Sec. 660.60 as follows:
0
a. Revise paragraph (d)(1)(v);
0
b. Remove paragraph (d)(1)(vii);
0
c. Redesignate paragraph (d)(1)(vi) as paragraph (d)(1)(vii); and
0
d. Add new paragraph (d)(1)(vi).
The revision and addition read as follows:
Sec. 660.60 Specifications and management measures.
* * * * *
(d) * * *
(1) * * *
(v) Close one or both of the whiting or non-whiting sectors of the
groundfish fishery upon that sector having exceeded its annual Chinook
salmon bycatch guideline and the reserve. The whiting sector includes
the Pacific whiting IFQ fishery, MS, and C/P sectors. The non-whiting
sector includes the midwater trawl, bottom trawl, and fixed gear
fisheries under the Shorebased IFQ Program, limited entry fixed gear
fisheries, open access fisheries, and recreational fisheries subject to
this provision as set out in Sec. 660.360(d).
(A) The whiting sector Chinook salmon bycatch guideline is 11,000
fish.
(B) The non-whiting sector Chinook salmon bycatch guideline is
5,500 fish.
(C) The reserve is 3,500 fish.
(vi) Close the whiting or non-whiting sector of the groundfish
fishery upon that sector having exceeded its annual Chinook salmon
bycatch guideline if the other sector has already been closed after
exceeding its Chinook salmon bycatch guideline and the reserve. The
whiting sector includes the Pacific whiting IFQ fishery, MS, and C/P
sectors. The non-whiting sector includes the midwater trawl, bottom
trawl, and fixed gear fisheries under the Shorebased IFQ Program,
limited entry fixed gear fisheries, open access fisheries, and
recreational fisheries subject to this provision as set out in Sec.
660.360(d).
* * * * *
0
7. Amend Sec. 660.71 as follows:
0
a. Redesignate paragraphs (k) through (n) as paragraphs (o) through
(r); and
0
b. Add new paragraphs (k) through (n) and paragraphs (s) through (v).
The additions read as follows:
Sec. 660.71 Latitude/longitude coordinates defining the 10-fm (18-m)
through 40-fm (73-m) depth contours.
* * * * *
(k) The 30 fm (55 m) depth contour around Santa Barbara Island off
the state of California is defined by straight lines connecting all of
the following points in the order stated:
(1) 33[deg]30.38' N lat., 119[deg]03.15' W long.;
(2) 33[deg]29.64' N lat., 119[deg]00.58' W long.;
(3) 33[deg]27.24' N lat., 119[deg]01.73' W long.;
(4) 33[deg]27.76' N lat., 119[deg]03.48' W long.;
(5) 33[deg]29.50' N lat., 119[deg]04.20' W long.; and
(6) 33[deg]30.38' N lat., 119[deg]03.15' W long.
(l) The 30 fm (55 m) depth contour around San Nicholas Island off
the state of California is defined by straight lines connecting all of
the following points in the order stated:
(1) 33[deg]18.39' N lat., 119[deg]38.87' W long.;
(2) 33[deg]18.63' N lat., 119[deg]27.52' W long.;
(3) 33[deg]15.24' N lat., 119[deg]20.10' W long.;
(4) 33[deg]13.27' N lat., 119[deg]20.10' W long.;
(5) 33[deg]12.16' N lat., 119[deg]26.82' W long.;
(6) 33[deg]13.20' N lat., 119[deg]31.87' W long.;
(7) 33[deg]15.70' N lat., 119[deg]38.87' W long.;
(8) 33[deg]17.52' N lat., 119[deg]40.15' W long.; and
(9) 33[deg]18.39' N lat., 119[deg]38.87' W long.
(m) The 30 fm (55 m) depth contour around Tanner Bank off the state
of California is defined by straight lines connecting all of the
following points in the order stated:
(1) 32[deg]43.02' N lat., 119[deg]08.52' W long.;
(2) 32[deg]41.81' N lat., 119[deg]06.20' W long.;
(3) 32[deg]40.67' N lat., 119[deg]06.82' W long.;
(4) 32[deg]41.62' N lat., 119[deg]09.46' W long.; and
(5) 32[deg]43.02' N lat., 119[deg]08.52' W long.
(n) The 30 fm (55 m) depth contour around Cortes Bank off the state
of California is defined by straight lines connecting all of the
following points in the order stated:
(1) 32[deg]29.73' N lat., 119[deg]12.95' W long.;
(2) 32[deg]28.17' N lat., 119[deg]07.04' W long.;
(3) 32[deg]26.27' N lat., 119[deg]04.14' W long.;
(4) 32[deg]25.22' N lat., 119[deg]04.77' W long.;
(5) 32[deg]28.60' N lat., 119[deg]14.15' W long.; and
(6) 32[deg]29.73' N lat., 119[deg]12.95' W long.
* * * * *
(s) The 40 fm (73 m) depth contour around Santa Barbara Island off
the state of California is defined by straight lines connecting all of
the following points in the order stated:
(1) 33[deg]30.87' N lat., 119[deg]02.43' W long.;
(2) 33[deg]29.87' N lat., 119[deg]00.34' W long.;
(3) 33[deg]27.08' N lat., 119[deg]01.65' W long.;
(4) 33[deg]27.64' N lat., 119[deg]03.45' W long.;
(5) 33[deg]29.12' N lat., 119[deg]04.55' W long.;
(6) 33[deg]29.66' N lat., 119[deg]05.49' W long.; and
(7) 33[deg]30.87' N lat., 119[deg]02.43' W long.
(t) The 40 fm (73 m) depth contour around Tanner Bank off the state
of California is defined by straight lines connecting all of the
following points in the order stated:
(1) 32[deg]43.40' N lat., 119[deg]08.56' W long.;
[[Page 47440]]
(2) 32[deg]41.36' N lat., 119[deg]05.02' W long.;
(3) 32[deg]40.07' N lat., 119[deg]05.59' W long.;
(4) 32[deg]41.51' N lat., 119[deg]09.76' W long.; and
(5) 32[deg]43.40' N lat., 119[deg]08.56' W long.
(u) The 40 fm (73 m) depth contour around San Nicholas Island off
the state of California is defined by straight lines connecting all of
the following points in the order stated:
(1) 33[deg]19.30' N lat., 119[deg]41.05' W long.;
(2) 33[deg]19.42' N lat., 119[deg]27.88' W long.;
(3) 33[deg]14.31' N lat., 119[deg]17.48' W long.;
(4) 33[deg]12.90' N lat., 119[deg]17.64' W long.;
(5) 33[deg]11.89' N lat., 119[deg]27.26' W long.;
(6) 33[deg]12.19' N lat., 119[deg]29.96' W long.;
(7) 33[deg]15.42' N lat., 119[deg]39.14' W long.;
(8) 33[deg]17.58' N lat., 119[deg]41.38' W long.; and
(9) 33[deg]19.30' N lat., 119[deg]41.05' W long.
(v) The 40 fm (73 m) depth contour around Cortes Bank off the state
of California is defined by straight lines connecting all of the
following points in the order stated:
(1) 32[deg]30.00' N lat., 119[deg]12.98' W long.;
(2) 32[deg]28.33' N lat., 119[deg]06.81' W long.;
(3) 32[deg]25.69' N lat., 119[deg]03.21' W long.;
(4) 32[deg]24.66' N lat., 119[deg]03.83' W long.;
(5) 32[deg]28.48' N lat., 119[deg]14.66' W long.; and
(6) 32[deg]30.00' N lat., 119[deg]12.98' W long.
0
8. Amend Sec. 660.72 as follows:
0
a. Redesignate paragraphs (k)(15) through (31) as (k)(17) through (33),
respectively; and
0
b. Add new paragraphs (k)(15) and (16).
The additions read as follows:
Sec. 660.72 Latitude/longitude coordinates defining the 50 fm (91 m)
through 75 fm (137 m) depth contours.
* * * * *
(k) * * *
(15) 33[deg]57.77' N lat., 119[deg]33.49' W long.;
(16) 33[deg]57.64' N lat., 119[deg]35.78' W long.;
* * * * *
0
9. Amend Sec. 660.73 as follows:
0
a. Revise paragraphs (a)(178), (a)(181), (a)(190) through (192), and
(d)(205) through (354);
0
b. Add paragraphs (d)(355) through (363);
0
c. Revise paragraphs (h)(281) through (313); and
0
d. Add paragraphs (h)(314) through (316).
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) * * *
(178) 40[deg]10.13' N lat., 124[deg]21.92' W long.;
* * * * *
(181) 40[deg]06.39' N lat., 124[deg]17.26' W long.;
* * * * *
(190) 40[deg]01.00' N lat., 124[deg]09.96' W long.;
(191) 39[deg]58.07' N lat., 124[deg]11.81' W long.;
(192) 39[deg]56.39' N lat., 124[deg]08.69' W long.;
* * * * *
(d) * * *
(205) 40[deg]02.67' N lat., 124[deg]11.83' W long.;
(206) 40[deg]02.70' N lat., 124[deg]10.57' W long.;
(207) 40[deg]04.08' N lat., 124[deg]10.09' W long.;
(208) 40[deg]04.08' N lat., 124[deg]09.10' W long.;
(209) 40[deg]01.23' N lat., 124[deg]08.91' W long.;
(210) 40[deg]01.18' N lat., 124[deg]09.92' W long.;
(211) 39[deg]58.05' N lat., 124[deg]11.87' W long.;
(212) 39[deg]56.39' N lat., 124[deg]08.70' W long.;
(213) 39[deg]54.64' N lat., 124[deg]07.31' W long.;
(214) 39[deg]53.87' N lat., 124[deg]07.95' W long.;
(215) 39[deg]52.42' N lat., 124[deg]08.18' W long.;
(216) 39[deg]49.64' N lat., 124[deg]06.05' W long.;
(217) 39[deg]49.30' N lat., 124[deg]04.60' W long.;
(218) 39[deg]48.49' N lat., 124[deg]03.86' W long.;
(219) 39[deg]47.73' N lat., 124[deg]04.59' W long.;
(220) 39[deg]42.50' N lat., 124[deg]00.60' W long.;
(221) 39[deg]34.23' N lat., 123[deg]56.82' W long.;
(222) 39[deg]33.00' N lat., 123[deg]56.44' W long.;
(223) 39[deg]30.96' N lat., 123[deg]56.00' W long.;
(224) 39[deg]31.34' N lat., 123[deg]56.71' W long.;
(225) 39[deg]32.03' N lat., 123[deg]57.44' W long.;
(226) 39[deg]31.43' N lat., 123[deg]58.16' W long.;
(227) 39[deg]05.56' N lat., 123[deg]57.24' W long.;
(228) 39[deg]01.75' N lat., 123[deg]56.83' W long.;
(229) 38[deg]59.52' N lat., 123[deg]55.95' W long.;
(230) 38[deg]58.98' N lat., 123[deg]56.57' W long.;
(231) 38[deg]57.50' N lat., 123[deg]56.57' W long.;
(232) 38[deg]53.91' N lat., 123[deg]56.00' W long.;
(233) 38[deg]42.57' N lat., 123[deg]46.60' W long.;
(234) 38[deg]28.72' N lat., 123[deg]35.61' W long.;
(235) 38[deg]28.01' N lat., 123[deg]36.47' W long.;
(236) 38[deg]20.94' N lat., 123[deg]31.26' W long.;
(237) 38[deg]15.94' N lat., 123[deg]25.33' W long.;
(238) 38[deg]10.95' N lat., 123[deg]23.19' W long.;
(239) 38[deg]05.52' N lat., 123[deg]22.90' W long.;
(240) 38[deg]08.46' N lat., 123[deg]26.23' W long.;
(241) 38[deg]06.95' N lat., 123[deg]28.03' W long.;
(242) 38[deg]06.25' N lat., 123[deg]29.70' W long.;
(243) 38[deg]04.57' N lat., 123[deg]31.37' W long.;
(244) 38[deg]02.32' N lat., 123[deg]31.09' W long.;
(245) 37[deg]59.97' N lat., 123[deg]28.43' W long.;
(246) 37[deg]58.10' N lat., 123[deg]26.69' W long.;
(247) 37[deg]55.46' N lat., 123[deg]27.05' W long.;
(248) 37[deg]51.51' N lat., 123[deg]24.86' W long.;
(249) 37[deg]45.01' N lat., 123[deg]12.09' W long.;
(250) 37[deg]35.67' N lat., 123[deg]01.56' W long.;
(251) 37[deg]26.62' N lat., 122[deg]56.21' W long.;
(252) 37[deg]14.41' N lat., 122[deg]49.07' W long.;
(253) 37[deg]11.00' N lat., 122[deg]45.87' W long.;
(254) 37[deg]07.00' N lat., 122[deg]41.97' W long.;
(255) 37[deg]03.19' N lat., 122[deg]38.31' W long.;
(256) 37[deg]00.99' N lat., 122[deg]35.51' W long.;
(257) 36[deg]58.31' N lat., 122[deg]27.56' W long.;
(258) 37[deg]00.54' N lat., 122[deg]24.74' W long.;
(259) 36[deg]57.81' N lat., 122[deg]24.65' W long.;
[[Page 47441]]
(260) 36[deg]58.54' N lat., 122[deg]21.67' W long.;
(261) 36[deg]56.52' N lat., 122[deg]21.70' W long.;
(262) 36[deg]55.37' N lat., 122[deg]18.45' W long.;
(263) 36[deg]52.16' N lat., 122[deg]12.17' W long.;
(264) 36[deg]51.53' N lat., 122[deg]10.67' W long.;
(265) 36[deg]48.05' N lat., 122[deg]07.59' W long.;
(266) 36[deg]47.35' N lat., 122[deg]03.27' W long.;
(267) 36[deg]50.71' N lat., 121[deg]58.17' W long.;
(268) 36[deg]48.89' N lat., 121[deg]58.90' W long.;
(269) 36[deg]47.70' N lat., 121[deg]58.76' W long.;
(270) 36[deg]48.37' N lat., 121[deg]51.15' W long.;
(271) 36[deg]45.74' N lat., 121[deg]54.18' W long.;
(272) 36[deg]45.50' N lat., 121[deg]57.73' W long.;
(273) 36[deg]44.02' N lat., 121[deg]58.55' W long.;
(274) 36[deg]38.84' N lat., 122[deg]01.32' W long.;
(275) 36[deg]35.63' N lat., 122[deg]00.98' W long.;
(276) 36[deg]32.47' N lat., 121[deg]59.17' W long.;
(277) 36[deg]32.52' N lat., 121[deg]57.62' W long.;
(278) 36[deg]30.16' N lat., 122[deg]00.55' W long.;
(279) 36[deg]24.56' N lat., 121[deg]59.19' W long.;
(280) 36[deg]22.19' N lat., 122[deg]00.30' W long.;
(281) 36[deg]20.62' N lat., 122[deg]02.93' W long.;
(282) 36[deg]18.89' N lat., 122[deg]05.18' W long.;
(283) 36[deg]14.45' N lat., 121[deg]59.44' W long.;
(284) 36[deg]13.73' N lat., 121[deg]57.38' W long.;
(285) 36[deg]14.41' N lat., 121[deg]55.45' W long.;
(286) 36[deg]10.25' N lat., 121[deg]43.08' W long.;
(287) 36[deg]07.67' N lat., 121[deg]40.92' W long.;
(288) 36[deg]02.51' N lat., 121[deg]36.76' W long.;
(289) 36[deg]01.04' N lat., 121[deg]36.68' W long.;
(290) 36[deg]00.00' N lat., 121[deg]35.15' W long.;
(291) 35[deg]57.84' N lat., 121[deg]33.10' W long.;
(292) 35[deg]45.57' N lat., 121[deg]27.26' W long.;
(293) 35[deg]39.02' N lat., 121[deg]22.86' W long.;
(294) 35[deg]25.92' N lat., 121[deg]05.52' W long.;
(295) 35[deg]16.26' N lat., 121[deg]01.50' W long.;
(296) 35[deg]07.60' N lat., 120[deg]56.49' W long.;
(297) 34[deg]57.77' N lat., 120[deg]53.87' W long.;
(298) 34[deg]42.30' N lat., 120[deg]53.42' W long.;
(299) 34[deg]37.69' N lat., 120[deg]50.04' W long.;
(300) 34[deg]30.13' N lat., 120[deg]44.45' W long.;
(301) 34[deg]27.00' N lat., 120[deg]39.24' W long.;
(302) 34[deg]24.71' N lat., 120[deg]35.37' W long.;
(303) 34[deg]21.63' N lat., 120[deg]24.86' W long.;
(304) 34[deg]24.39' N lat., 120[deg]16.65' W long.;
(305) 34[deg]22.48' N lat., 119[deg]56.42' W long.;
(306) 34[deg]18.54' N lat., 119[deg]46.26' W long.;
(307) 34[deg]16.37' N lat., 119[deg]45.12' W long.;
(308) 34[deg]15.91' N lat., 119[deg]47.29' W long.;
(309) 34[deg]13.80' N lat., 119[deg]45.40' W long.;
(310) 34[deg]11.69' N lat., 119[deg]41.80' W long.;
(311) 34[deg]09.98' N lat., 119[deg]31.87' W long.;
(312) 34[deg]08.12' N lat., 119[deg]27.71' W long.;
(313) 34[deg]06.35' N lat., 119[deg]32.65' W long.;
(314) 34[deg]06.80' N lat., 119[deg]40.08' W long.;
(315) 34[deg]07.48' N lat., 119[deg]47.54' W long.;
(316) 34[deg]08.21' N lat., 119[deg]54.90' W long.;
(317) 34[deg]06.85' N lat., 120[deg]05.60' W long.;
(318) 34[deg]07.03' N lat., 120[deg]10.47' W long.;
(319) 34[deg]08.77' N lat., 120[deg]18.46' W long.;
(320) 34[deg]11.89' N lat., 120[deg]28.09' W long.;
(321) 34[deg]12.53' N lat., 120[deg]29.82' W long.;
(322) 34[deg]09.02' N lat., 120[deg]37.47' W long.;
(323) 34[deg]01.01' N lat., 120[deg]31.17' W long.;
(324) 33[deg]58.07' N lat., 120[deg]28.33' W long.;
(325) 33[deg]53.37' N lat., 120[deg]14.43' W long.;
(326) 33[deg]50.53' N lat., 120[deg]07.20' W long.;
(327) 33[deg]45.88' N lat., 120[deg]04.26' W long.;
(328) 33[deg]38.19' N lat., 119[deg]57.85' W long.;
(329) 33[deg]38.19' N lat., 119[deg]50.42' W long.;
(330) 33[deg]42.36' N lat., 119[deg]49.60' W long.;
(331) 33[deg]53.95' N lat., 119[deg]53.81' W long.;
(332) 33[deg]55.99' N lat., 119[deg]41.40' W long.;
(333) 33[deg]58.48' N lat., 119[deg]27.90' W long.;
(334) 33[deg]59.24' N lat., 119[deg]23.61' W long.;
(335) 33[deg]59.35' N lat., 119[deg]21.71' W long.;
(336) 33[deg]59.94' N lat., 119[deg]19.57' W long.;
(337) 34[deg]04.48' N lat., 119[deg]15.32' W long.;
(338) 34[deg]02.80' N lat., 119[deg]12.95' W long.;
(339) 34[deg]02.39' N lat., 119[deg]07.17' W long.;
(340) 34[deg]03.75' N lat., 119[deg]04.72' W long.;
(341) 34[deg]01.82' N lat., 119[deg]03.24' W long.;
(342) 33[deg]59.33' N lat., 119[deg]03.49' W long.;
(343) 33[deg]59.01' N lat., 118[deg]59.56' W long.;
(344) 33[deg]59.51' N lat., 118[deg]57.25' W long.;
(345) 33[deg]58.83' N lat., 118[deg]52.50' W long.;
(346) 33[deg]58.55' N lat., 118[deg]41.86' W long.;
(347) 33[deg]55.10' N lat., 118[deg]34.25' W long.;
(348) 33[deg]54.30' N lat., 118[deg]38.71' W long.;
(349) 33[deg]50.88' N lat., 118[deg]37.02' W long.;
(350) 33[deg]39.78' N lat., 118[deg]18.40' W long.;
(351) 33[deg]35.50' N lat., 118[deg]16.85' W long.;
(352) 33[deg]32.46' N lat., 118[deg]10.90' W long.;
(353) 33[deg]34.11' N lat., 117[deg]54.07' W long.;
(354) 33[deg]31.61' N lat., 117[deg]49.30' W long.;
(355) 33[deg]16.36' N lat., 117[deg]35.48' W long.;
(356) 33[deg]06.81' N lat., 117[deg]22.93' W long.;
(357) 32[deg]59.28' N lat., 117[deg]19.69' W long.;
(358) 32[deg]55.37' N lat., 117[deg]19.55' W long.;
(359) 32[deg]53.35' N lat., 117[deg]17.05' W long.;
(360) 32[deg]53.36' N lat., 117[deg]19.12' W long.;
(361) 32[deg]46.42' N lat., 117[deg]23.45' W long.;
(362) 32[deg]42.71' N lat., 117[deg]21.45' W long.; and
(363) 32[deg]34.54' N lat., 117[deg]23.04' W long.
* * * * *
[[Page 47442]]
(h) * * *
(281) 34[deg]07.10' N lat., 120[deg]10.37' W long.;
(282) 34[deg]11.07' N lat., 120[deg]25.03' W long.;
(283) 34[deg]09.00' N lat., 120[deg]18.40' W long.;
(284) 34[deg]13.16' N lat., 120[deg]29.40' W long.;
(285) 34[deg]09.41' N lat., 120[deg]37.75' W long.;
(286) 34[deg]03.15' N lat., 120[deg]34.71' W long.;
(287) 33[deg]57.09' N lat., 120[deg]27.76' W long.;
(288) 33[deg]51.00' N lat., 120[deg]09.00' W long.;
(289) 33[deg]38.16' N lat., 119[deg]59.23' W long.;
(290) 33[deg]37.04' N lat., 119[deg]50.17' W long.;
(291) 33[deg]42.28' N lat., 119[deg]48.85' W long.;
(292) 33[deg]53.96' N lat., 119[deg]53.77' W long.;
(293) 33[deg]55.88' N lat., 119[deg]41.05' W long.;
(294) 33[deg]59.18' N lat., 119[deg]23.64' W long.;
(295) 33[deg]59.26' N lat., 119[deg]21.92' W long.;
(296) 33[deg]59.94' N lat., 119[deg]19.57' W long.;
(297) 34[deg]03.12' N lat., 119[deg]15.51' W long.;
(298) 34[deg]01.97' N lat., 119[deg]07.28' W long.;
(299) 34[deg]03.60' N lat., 119[deg]04.71' W long.;
(300) 33[deg]59.30' N lat., 119[deg]03.73' W long.;
(301) 33[deg]58.87' N lat., 118[deg]59.37' W long.;
(302) 33[deg]58.08' N lat., 118[deg]41.14' W long.;
(303) 33[deg]50.93' N lat., 118[deg]37.65' W long.;
(304) 33[deg]39.54' N lat., 118[deg]18.70' W long.;
(305) 33[deg]35.42' N lat., 118[deg]17.14' W long.;
(306) 33[deg]32.15' N lat., 118[deg]10.84' W long.;
(307) 33[deg]33.71' N lat., 117[deg]53.72' W long.;
(308) 33[deg]31.17' N lat., 117[deg]49.11' W long.;
(309) 33[deg]16.53' N lat., 117[deg]36.13' W long.;
(310) 33[deg]06.77' N lat., 117[deg]22.92' W long.;
(311) 32[deg]58.94' N lat., 117[deg]20.05' W long.;
(312) 32[deg]55.83' N lat., 117[deg]20.15' W long.;
(313) 32[deg]46.29' N lat., 117[deg]23.89' W long.;
(314) 32[deg]42.00' N lat., 117[deg]22.16' W long.;
(315) 32[deg]39.47' N lat., 117[deg]27.78' W long.; and
(316) 32[deg]34.83' N lat., 117[deg]24.69' W long.
* * * * *
0
10. Tables 1a to part 660, subpart C through 1d to part 660, subpart C
are revised to read as follows:
Sec.
* * * * *
Table 1a to Part 660, Subpart C--2019, Specifications of OFL, ABC,
ACL, ACT and Fishery HG (Weights in Metric Tons)
Table 1b. to Part 660, Subpart C--2019, Allocations by Species or
Species Group (Weight in Metric Tons)
Table 1c. to Part 660, Subpart C--Sablefish North of 36[deg] N lat.
Allocations, 2019
Table 1d. to Part 660, Subpart C--At-Sea Whiting Fishery Annual Set-
Asides, 2019
* * * * *
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0
11. Tables 2a to part 660, subpart C through 2d to part 660, supbart C
are revised to read as follows:
Sec.
* * * * *
Table 2a. to Part 660, Subpart C--2020, and Beyond, Specifications
of OFL, ABC, ACL, ACT and Fishery Harvest Guidelines (Weights in
Metric Tons)
Table 2b. to Part 660, Subpart C--2020, and Beyond, Allocations by
Species or Species Group [Weight in Metric Tons]
Table 2c. to Part 660, Subpart C--Sablefish North of 36[deg] N lat.
Allocations, 2020 and Beyond
Table 2d. to Part 660, Subpart C--At-Sea Whiting Fishery Annual Set-
Asides, 2020 and Beyond
* * * * *
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0
12. In Sec. 660.130, add paragraph (c)(2)(ii), revise paragraphs
(d)(1)(ii) and (e)(6), and add paragraph (e)(8) to read as follows:
Sec. 660.130 Trawl fishery--management measures.
* * * * *
(c) * * *
(2) * * *
(ii) The use of selective flatfish trawl gear is required inside
the Klamath River Salmon Conservation Zone (defined at Sec.
660.131(c)(1)) and the Columbia River Salmon Conservation Zone (defined
at Sec. 660.131(c)(2)).
* * * * *
(d) * * *
(1) * * *
(ii) North of 40[deg]10' N lat. POP, yellowtail rockfish,
Washington cabezon/kelp greenling complex, Oregon cabezon/kelp
greenling complex, cabezon off California;
* * * * *
(e) * * *
(6) Bycatch reduction areas (BRAs). Vessels using midwater
groundfish trawl gear during the applicable Pacific whiting primary
season may be prohibited from fishing shoreward of a boundary line
approximating the 75 fm (137 m), 100 fm (183 m), 150 fm (274 m), or 200
fm (366 m) depth contours.
* * * * *
(8) Salmon conservation zones. Fishing with midwater trawl gear and
bottom trawl gear, other than selective flatfish trawl gear, is
prohibited in the following areas:
(i) Klamath River Salmon Conservation Zone. The ocean area
surrounding the Klamath River mouth bounded on the north by
41[deg]38.80' N lat. (approximately 6 nm north of the Klamath River
mouth), on the west by 124[deg]23' W long. (approximately 12 nm from
shore), and on the south by 41[deg]26.80' N lat. (approximately 6 nm
south of the Klamath River mouth).
(ii) Columbia River Salmon Conservation Zone. The ocean area
surrounding the Columbia River mouth bounded by a line extending for 6
nm due west from North Head along 46[deg]18' N lat. to 124[deg]13.30' W
long., then southerly along a line of 167 True to 46[deg]11.10' N lat.
and 124[deg]11' W long. (Columbia River Buoy), then northeast along Red
Buoy Line to the tip of the south jetty.
* * * * *
0
13. In Sec. 660.131, remove and reserve paragraph (c)(3) and add
paragraph (i).
The addition reads as follows:
Sec. 660.131 Pacific whiting fishery management measures.
* * * * *
(i) Salmon bycatch. This fishery may be closed through automatic
action at Sec. 660.60(d)(1)(v) and (vi).
0
14. In Sec. 660.140, revise paragraphs (d)(1)(ii)(D), (e)(4)(i),
(g)(1), (h)(1)(i)(A)(3), and (l)(2) to read as follows:
Sec. 660.140 Shorebased IFQ Program.
* * * * *
(d) * * *
(1) * * *
(ii) * * *
(D) For the trawl fishery, NMFS will issue QP based on the
following shorebased trawl allocations:
----------------------------------------------------------------------------------------------------------------
2019 2020
Shorebased Shorebased
IFQ species Area trawl trawl
allocation allocation
(mt) (mt)
----------------------------------------------------------------------------------------------------------------
Arrowtooth flounder........................... Coastwide....................... 12,735.1 10,052.3
Bocaccio...................................... South of 40[deg]10' N lat....... 800.7 767.1
Canary rockfish............................... Coastwide....................... 946.9 887.8
Chilipepper................................... South of 40[deg]10' N lat....... 1,838.3 1,743.8
COWCOD........................................ South of 40[deg]10' N lat....... 2.2 2.2
Darkblotched rockfish......................... Coastwide....................... 658.4 703.4
Dover sole.................................... Coastwide....................... 45,979.2 45,979.2
English sole.................................. Coastwide....................... 9,375.1 9,417.9
Lingcod....................................... North of 40[deg]10' N lat....... 2,051.9 1,903.4
Lingcod....................................... South of 40[deg]10' N lat....... 462.5 386.0
Longspine thornyhead.......................... North of 34[deg]27' N lat....... 2,420.0 2,293.6
Minor Shelf Rockfish complex.................. North of 40[deg]10' N lat....... 1,155.2 1,151.6
Minor Shelf Rockfish complex.................. South of 40[deg]10' N lat....... 188.6 188.6
Minor Slope Rockfish complex.................. North of 40[deg]10' N lat....... 1,248.8 1,237.5
Minor Slope Rockfish complex.................. South of 40[deg]10' N lat....... 1,049.1 455.4
Other Flatfish complex........................ Coastwide....................... 5,603.7 5,192.4
Pacific cod................................... Coastwide....................... 1,034.1 1,034.1
Pacific ocean perch........................... North of 40[deg]10' N lat....... 3,697.3 3,602.2
Pacific whiting............................... Coastwide....................... TBD TBD
Petrale sole.................................. Coastwide....................... 2,453.0 2,393.2
Sablefish..................................... North of 36[deg] N lat.......... 2,581.3 2,636.8
Sablefish..................................... South of 36[deg] N lat.......... 834.0 851.7
Shortspine thornyhead......................... North of 34[deg]27' N lat....... 1,511.8 1,498.5
Shortspine thornyhead......................... South of 34[deg]27' N lat....... 50.0 50.0
Splitnose rockfish............................ South of 40[deg]10' N lat....... 1,646.7 1,628.7
[[Page 47471]]
Starry flounder............................... Coastwide....................... 211.6 211.6
Widow rockfish................................ Coastwide....................... 9,928.8 9,387.1
YELLOWEYE ROCKFISH............................ Coastwide....................... 3.4 3.4
Yellowtail rockfish........................... North of 40[deg]10' N lat....... 4,057.7 3,810.4
----------------------------------------------------------------------------------------------------------------
* * * * *
(e) * * *
(4) * * *
(i) Vessel limits. For each IFQ species or species group specified
in this paragraph, vessel accounts may not have QP or IBQ pounds in
excess of the annual QP vessel limit in any year. The annual QP vessel
limit is calculated as all QPs transferred in minus all QPs transferred
out of the vessel account.
------------------------------------------------------------------------
Annual QP
Species category vessel limit
(in percent)
------------------------------------------------------------------------
Arrowtooth flounder..................................... 20
Bocaccio S of 40[deg]10' N lat.......................... 15.4
Canary rockfish......................................... 10
Chilipepper S of 40[deg]10' N lat....................... 15
Cowcod S of 40[deg]10' N lat............................ 17.7
Darkblotched rockfish................................... 6.8
Dover sole.............................................. 3.9
English sole............................................ 7.5
Lingcod:
N of 40[deg]10' N lat................................. 5.3
S of 40[deg]10' N lat................................. 13.3
Longspine thornyhead:
N of 34[deg]27' N lat................................. 9
Minor rockfish complex N of 40[deg]10' N lat:
Shelf species......................................... 7.5
Slope species......................................... 7.5
Minor rockfish complex S of 40[deg]10' N lat:
Shelf species......................................... 13.5
Slope species......................................... 9
Other Flatfish complex.................................. 15
Pacific cod............................................. 20
Pacific halibut (IBQ) N of 40[deg]10' N lat............. 14.4
Pacific ocean perch N of 40[deg]10' N lat............... 6
Pacific whiting (shoreside)............................. 15
Petrale sole............................................ 4.5
Sablefish:
N of 36[deg] N lat (Monterey north)................... 4.5
S of 36[deg] N lat (Conception area).................. 15
Shortspine thornyhead:
N of 34[deg]27' N lat................................. 9
S of 34[deg]27' N lat................................. 9
Splitnose rockfish S of 40[deg]10' N lat................ 15
Starry flounder......................................... 20
Widow rockfish.......................................... 8.5
Yelloweye rockfish...................................... 11.4
Yellowtail rockfish N of 40[deg]10' N lat............... 7.5
Non-whiting groundfish species.......................... 3.2
------------------------------------------------------------------------
* * * * *
(g) * * *
(1) General. Shorebased IFQ Program vessels may discard IFQ
species/species groups, and the discard mortality must be accounted for
and deducted from QP in the vessel account. With the exception of
vessels on Pacific whiting IFQ trips engaged in maximized retention,
prohibited and protected species must be discarded at sea; Pacific
halibut must be discarded as soon as practicable and the discard
mortality must be accounted for and deducted from IBQ pounds in the
vessel account. Non-IFQ species and non-groundfish species may be
discarded at sea. The sorting of catch, the weighing and discarding of
any IBQ and IFQ species, and the retention of IFQ species must be
monitored by the observer.
* * * * *
(h) * * *
(1) * * *
(i) * * *
(A) * * *
(3) Is exempt from the requirement to maintain observer coverage as
specified in this paragraph while remaining docked in port when the
observer makes available to the catch monitor an Observer Program
reporting form documenting the weight and number of any overfished
species listed under a rebuilding plan at Sec. 660.40 retained during
that trip and which documents any discrepancy the vessel operator and
observer may have in the weights and number of the overfished species,
unless modified inseason under routine management measures at Sec.
660.60(c)(1).
* * * * *
(l) * * *
(2) AMP QP pass through. The 10 percent of non-whiting QS will be
reserved for the AMP, but the resulting AMP QP will be issued to all QS
permit owners in proportion to their non-whiting QS until an
alternative use of AMP QP is implemented.
0
15. In Sec. 660.150, revise paragraph (c)(1)(ii) to read as follows:
Sec. 660.150 Mothership (MS) Coop Program.
* * * * *
(c) * * *
(1) * * *
(ii) Species with set-asides for the MS and C/P Coop Programs, as
described in Table 1d and Table 2d, subpart C.
* * * * *
0
16. In Sec. 660.160, revise paragraph (c)(1)(ii) to read as follows:
Sec. 660.160 Catcher/processor (C/P) Coop Program.
* * * * *
(c) * * *
(1) * * *
(ii) Species with set-asides for the MS and C/P Programs, as
described in Table 1d and 2d, subpart C.
* * * * *
0
17. Revise Tables 1 (North) and 1 (South) to part 660, subpart D to
read as follows:
Table 1 (North) to Part 660, Subpart D--Limited Entry Trawl
Rockfish Conservation Areas and Landing Allowances for non-IFQ Species
and Pacific Whiting North of 40[deg]10' N Lat.
[[Page 47472]]
[GRAPHIC] [TIFF OMITTED] TP19SE18.029
Table 1 (South) to Part 660, Subpart D--Limited Entry Trawl
Rockfish Conservation Areas and Landing Allowances for non-IFQ Species
and Pacific Whiting South of 40[deg]10' N Lat.
[[Page 47473]]
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0
18. In Sec. 660.230, revise paragraphs (c)(2)(ii) and (d)(10)(ii) and
add paragraph (f) to read as follows:
Sec. 660.230 Fixed gear fishery--management measures.
* * * * *
(c) * * *
(2) * * *
(ii) North of 40[deg]10' N lat.--POP, yellowtail rockfish, cabezon
(California), Washington cabezon/kelp greenling complex, Oregon
cabezon/kelp greenling complex;
* * * * *
(d) * * *
(10) * * *
(ii) Fishing for rockfish and lingcod is permitted shoreward of the
40 fm (73 m) depth contour within the CCAs when trip limits authorize
such fishing, and provided a valid declaration report as required at
Sec. 660.13(d), subpart C, has been filed with NMFS OLE.
* * * * *
[[Page 47474]]
(f) Salmon bycatch. This fishery may be closed through automatic
action at Sec. 660.60(d)(1)(v) and (vi).
0
19. 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 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 2019, the
following annual limits are in effect: Tier 1 at 47,637 lb (21,608 kg),
Tier 2 at 21,653 lb (9,822 kg), and Tier 3 at 12,373 lb (5,612 kg). In
2020 and beyond, the following annual limits are in effect: Tier 1 at
48,642 lb (22,064 kg), Tier 2 at 22,110 lb (10,029 kg), and Tier 3 at
12,634 lb (5,731 kg).
* * * * *
0
20. Revise Tables 2 (North) and 2 (South) to part 660, subpart E, to
read as follows:
Table 2 (North) to Part 660, Subpart E--Non-Trawl Rockfish
Conservation Areas and Trip Limits for Limited Entry Fixed Gear North
of 40[deg]10' N Lat.
[[Page 47475]]
[GRAPHIC] [TIFF OMITTED] TP19SE18.031
Table 2 (South) to Part 660, Subpart E--Non-Trawl Rockfish
Conservation Areas and Trip Limits for Limited Entry Fixed Gear South
of 40[deg]10' N Lat.
[[Page 47476]]
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[[Page 47477]]
0
21. In Sec. 660.330, revise paragraphs (c)(2)(ii) and (d)(11)(ii) and
add paragraph (f) to read as follows:
Sec. 660.330 Open access fishery--management measures.
* * * * *
(c) * * *
(2) * * *
(ii) North of 40[deg]10' N lat.--POP, yellowtail rockfish, cabezon
(California), Washington cabezon/kelp greenling complex, Oregon
cabezon/kelp greenling complex;
* * * * *
(d) * * *
(11) * * *
(ii) Fishing for rockfish and lingcod is permitted shoreward of the
40 fm (73 m) depth contour within the CCAs when trip limits authorize
such fishing, and provided a valid declaration report as required at
Sec. 660.13(d), has been filed with NMFS OLE.
* * * * *
(f) Salmon bycatch. This fishery may be closed through automatic
action at Sec. 660.60(d)(1)(v) and (d)(1)(vi).
0
22. In Sec. 660.333, revise paragraph (c)(3) to read as follows:
Sec. 660.333 Open access non-groundfish trawl fishery--management
measures.
* * * * *
(c) * * *
(3) The landing includes California halibut of a size required by
California Fish and Game Code section 8392, which states: ``No
California halibut may be taken, possessed or sold which measures less
than 22 in (56 cm) in total length. Total length means the shortest
distance between the tip of the jaw or snout, whichever extends
farthest while the mouth is closed, and the tip of the longest lobe of
the tail, measured while the halibut is lying flat in natural repose,
without resort to any force other than the swinging or fanning of the
tail.''
* * * * *
0
23. Revise Tables 3 (North) and 3 (South) in part 660, subpart F, to
read as follows:
Table 3 (North) to Part 660, Subpart F--Non-Trawl Rockfish
Conservation Areas and Trip Limits for Open Access Gears North of
40[deg]10' N Lat.
[[Page 47478]]
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[[Page 47479]]
[GRAPHIC] [TIFF OMITTED] TP19SE18.034
Table 3 (South) to Part 660, Subpart F--Non-Trawl Rockfish
Conservation Areas and Trip Limits for Open Access Gears South of
40[deg]10' N Lat.
[[Page 47480]]
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BILLING CODE 3510-22-C
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24. Amend Sec. 660.360 as follows:
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a. Revise paragraphs (c)(1) introductory text, (c)(1)(i)(D)(1) through
(3), (c)(1)(ii) through (iv), (c)(2)(i)(B), (c)(3)(i)(A) through (C),
(c)(3)(ii)(D), (c)(3)(iii)(B), (c)(3)(iii)(D), (c)(3)(iv), and
(c)(3)(v)(A) and (B); and
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b. Add paragraph (d).
The revisions and addition 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 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 3 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) * * *
(D) * * *
(1) West of the Bonilla-Tatoosh line between the U.S. border with
Canada and the Queets River (Washington state Marine Area 3 and 4),
recreational fishing for groundfish is prohibited seaward of a boundary
line approximating the 20 fm (37 m) depth contour from June 1 through
Labor Day, except on days when the Pacific halibut fishery is open in
this area it is lawful to retain lingcod, Pacific cod, and sablefish
seaward of the 20 fm (37 m) boundary. Yellowtail and widow rockfish can
be retained seaward of 20 fm (37 m) in the months of July and August on
days open to the recreational salmon fishery. Days open to Pacific
halibut recreational fishing off Washington and days open to
recreational fishing for salmon are announced on the NMFS hotline at
(206) 526-6667 or (800) 662-9825. Coordinates for the boundary line
approximating the 20 fm (37 m) depth contour are listed in Sec.
660.71, subpart C.
(2) Between the Queets River (47[deg]31.70' N lat.) and Leadbetter
Point (46[deg]38.17' N lat.) (Washington state Marine Area 2),
recreational fishing for lingcod is prohibited seaward of a boundary
line approximating the 30 fm (55 m) depth contour from the second
[[Page 47482]]
Saturday in March through May 31 with the following exceptions:
Recreational fishing for lingcod is permitted within the RCA on days
that the primary halibut fishery is open; recreational fishing for
lingcod is allowed on Sundays in May, but only if the Pacific halibut
recreational fishery in this area is scheduled to be open for less than
four days. In addition to the RCA described above, between the Queets
River (47[deg]31.70' N lat.) and Leadbetter Point (46[deg]38.17' N
lat.) (Washington state Marine Area 2), recreational fishing for
lingcod is prohibited January 1 through May 31, June 16 through August
31, and September 16 through December 31 seaward of a straight line
connecting all of the following points in the order stated:
47[deg]31.70' N lat., 124[deg]45.00' W long.; 46[deg]38.17' N lat.,
124[deg]30.00' W long. with the following exceptions: On days that the
primary halibut fishery is open lingcod may be taken, retained and
possessed within the lingcod area closure; if the Pacific halibut
recreational fishery is scheduled to be open less than four days,
lingcod may be taken, retained, and possessed within the lingcod area
closure on Sundays in May. Days open to Pacific halibut recreational
fishing off Washington are announced on the NMFS hotline at (206) 526-
6667 or (800) 662-9825. For additional regulations regarding the
Washington recreational lingcod fishery, see paragraph (c)(1)(iv) of
this section. Coordinates for the boundary line approximating the 30 fm
(55 m) depth contour are listed in Sec. 660.71.
(3) Between Leadbetter Point (46[deg]38.17' N lat.) and the
Columbia River (46[deg]16.00' N lat.) (Marine Area 1), when Pacific
halibut are onboard the vessel, no groundfish may be taken and
retained, possessed or landed, except sablefish, flatfish species
(except halibut), Pacific cod, and lingcod from May 1 through September
30. Except that taking, retaining, possessing or landing incidental
halibut with groundfish on board is allowed in the nearshore area on
days not open to all-depth Pacific halibut fisheries in the area
shoreward of the boundary line approximating the 30 fathom (55 m) depth
contour extending from Leadbetter Point, WA (46[deg]38.17' N lat.,
124[deg]15.88' W long.) to the Columbia River (46[deg]16.00' N lat.,
124[deg]15.88' W long.) and from there, connecting to the boundary line
approximating the 40 fathom (73 m) depth contour in Oregon. Nearshore
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 halibut hotline, 1-800-662-9825. Between
Leadbetter Point (46[deg]38.17' N lat. 124[deg]21.00' W long.) and
46[deg]33.00' N lat. 124[deg]21.00' W long., recreational fishing for
lingcod is prohibited year round seaward of a straight line connecting
all of the following points in the order stated: 46[deg]38.17' N lat.,
124[deg]21.00' W long.; and 46[deg]33.00' N lat., 124[deg]21.00' W
long.
(ii) Rockfish. In areas of the EEZ seaward of Washington
(Washington Marine Areas 1-4) that are open to recreational groundfish
fishing, there is a 7 rockfish per day bag limit. Taking and retaining
yelloweye rockfish is prohibited in all Marine areas.
(iii) Cabezon. In areas of the EEZ seaward of Washington
(Washington Marine Areas 1-4) that are open to recreational groundfish
fishing, there is a 1 cabezon per day bag limit.
(iv) Lingcod. In areas of the EEZ seaward of Washington (Washington
Marine Areas 1-4) that are open to recreational groundfish fishing and
when the recreational season for lingcod is open, there is a bag limit
of 2 lingcod per day. The recreational fishing season for lingcod is
open from the second Saturday in March through the third Saturday in
October.
(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 June 1 through August 31,
recreational fishing for groundfish is prohibited seaward of a
recreational RCA boundary line approximating the 40 fm (73 m) depth
contour, except that fishing for flatfish (other than Pacific halibut)
is allowed seaward of the 40 fm (73 m) depth contour when recreational
fishing for groundfish is permitted. Coordinates for the boundary line
approximating the 40 fm (73 m) depth contour are listed at Sec.
660.71.
* * * * *
(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 ``Other
Flatfish,'' 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.
(1) Between 42[deg] N lat. (California/Oregon border) and
40[deg]10' N lat. (Northern Management Area), recreational fishing for
all groundfish (except petrale sole, starry flounder, and ``Other
Flatfish'' as specified in paragraph (c)(3)(iv) of this section) is
closed from January 1 through April 30; is prohibited seaward of the 30
fm (55 m) depth contour along the mainland coast and along islands and
offshore seamounts from May 1 through October 31 (shoreward of 30 fm is
open); and is open at all depths from November 1 through December 31.
Coordinates for the boundary line approximating the 30 fm (55 m) depth
contour are listed in Sec. 660.71.
(2) Between 40[deg]10' N lat. and 38[deg]57.50' N lat. (Mendocino
Management Area), recreational fishing for all groundfish (except
petrale sole, starry flounder, and ``Other Flatfish'' as specified in
paragraph (c)(3)(iv) of this section) is closed from January 1 through
April 30; prohibited seaward of the 20 fm (37 m) depth contour along
the mainland coast and along islands and offshore seamounts from May 1
through October 31 (shoreward of 20 fm is open), and is open at all
depths from November 1 through December 31.
(3) Between 38[deg]57.50' N lat. and 37[deg]11' N lat. (San
Francisco Management Area), recreational fishing
[[Page 47483]]
for all groundfish (except petrale sole, starry flounder, and ``Other
Flatfish'' as specified in paragraph (c)(3)(iv) of this section) is
closed from January 1 through April 1; is prohibited seaward of the
boundary line approximating the 40 fm (73 m) depth contour along the
mainland coast and along islands and offshore seamounts from April 1
through December 31. Closures around Cordell Banks (see paragraph
(c)(3)(i)(C) of this section) also apply in this area. Coordinates for
the boundary line approximating the 40 fm (73 m) depth contour are
listed in Sec. 660.71.
(4) Between 37[deg]11' N lat. and 34[deg]27' N lat. (Central
Management Area), recreational fishing for all groundfish (except
petrale sole, starry flounder, and ``Other Flatfish'' as specified in
paragraph (c)(3)(iv) of this section) is closed from January 1 through
March 31; and is prohibited seaward of a boundary line approximating
the 50 fm (91 m) depth contour along the mainland coast and along
islands and offshore seamounts from April 1 through December 31.
Coordinates for the boundary line approximating the 50 fm (91 m) depth
contour are specified in Sec. 660.72.
(5) South of 34[deg]27' N lat. (Southern Management Area),
recreational fishing for all groundfish (except California
scorpionfish, ``Other Flatfish,'' petrale sole, and starry flounder) is
closed entirely from January 1 through February 28. Recreational
fishing for all groundfish (except ``Other Flatfish,'' petrale sole,
and starry flounder, as specified in paragraph (c)(3)(iv) of this
section) is prohibited seaward of a boundary line approximating the 75
fm (137 m) depth contour from March 1 through December 31 along the
mainland coast and along islands and offshore seamounts, except in the
CCAs where fishing is prohibited seaward of the 40 fm (73 m) depth
contour when the fishing season is open (see paragraph (c)(3)(i)(B) of
this section). Coordinates for the boundary lines approximating the
depth contours are specified at Sec. Sec. 660.71 through 660.74.
(B) Cowcod conservation areas. The latitude and longitude
coordinates of the Cowcod Conservation Areas (CCAs) boundaries are
specified at Sec. 660.70. In general, recreational fishing for all
groundfish is prohibited within the CCAs, except that fishing for
petrale sole, starry flounder, and ``Other Flatfish'' is permitted
within the CCAs as specified in paragraph (c)(3)(iv) of this section.
However, recreational fishing for the following species is prohibited
seaward of the 40 fm (37 m) depth contour when the season for those
species is open south of 34[deg]27' N lat.: Minor Nearshore Rockfish,
cabezon, kelp greenling, lingcod, California scorpionfish, and shelf
rockfish. Retention of yelloweye rockfish, bronzespotted rockfish and
cowcod is prohibited within the CCA. [Note: California state
regulations also permit recreational fishing for California sheephead,
ocean whitefish, and all greenlings of the genus Hexagrammos shoreward-
of the 40 fm (73 m) depth contour in the CCAs when the season for the
RCG complex is open south of 34[deg]27' N lat.] It is unlawful to take
and retain, possess, or land groundfish taken within the CCAs, except
for species authorized in this section.
(C) Cordell Banks. Recreational fishing for groundfish is
prohibited in waters less than 100 fm (183 m) around Cordell Banks as
defined by specific latitude and longitude coordinates at Sec. 660.70,
subpart C, except that recreational fishing for petrale sole, starry
flounder, and ``Other Flatfish'' is permitted around Cordell Banks as
specified in paragraph (c)(3)(iv) of this section.
* * * * *
(ii) * * *
(D) Dressing/filleting. Cabezon, kelp greenling, and rock greenling
taken in the recreational fishery may not be filleted at sea. Rockfish
skin may not be removed when filleting or otherwise dressing rockfish
taken in the recreational fishery.
* * * * *
(iii) * * *
(B) Bag limits, hook limits. In times and areas when the
recreational season for lingcod is open, there is a limit of 2 hooks
and 1 line when fishing for lingcod. 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.
(1) The bag limit between 42[deg] N lat. (California/Oregon border)
and 40[deg]10' N lat. (Northern Management Area) is 2 lingcod per day.
(2) The bag limit between 40[deg]10' N lat. and the U.S. border
with Mexico (Mendocino Management Area, San Francisco Management Area,
Central Management Area, and Southern Management Area) is 1 lingcod per
day.
* * * * *
(D) Dressing/filleting. Lingcod filets may be no smaller than 14 in
(36 cm) in length. Each fillet shall bear an intact 1 in (2.6 cm)
square patch of skin.
(iv) ``Other Flatfish,'' petrale sole, and starry flounder.
Coastwide off California, recreational fishing for ``Other Flatfish,''
petrale sole, and starry flounder, is permitted both shoreward of and
within the closed areas described in paragraph (c)(3)(i) of this
section. ``Other Flatfish'' are defined at Sec. 660.11, subpart C, and
include butter sole, curlfin sole, flathead sole, Pacific sanddab, rex
sole, rock sole, and sand sole. ``Other Flatfish,'' are subject to the
overall 20-fish bag limit for all species of finfish, of which there
may be no more than 10 fish of any one species; there is no daily bag
limit for petrale sole, starry flounder and Pacific sanddab. There are
no size limits for ``Other Flatfish,'' petrale sole, and starry
flounder. ``Other Flatfish'', petrale sole, and starry flounder may be
filleted at sea. Fillets may be of any size, but must bear intact a
one-inch square patch of skin.
(v) * * *
(A) Seasons. When recreational fishing for California scorpionfish
is open, it is permitted only outside of the recreational RCAs
described in paragraph (c)(3)(i) of this section.
(1) Between 40[deg]10' N lat. and 38[deg]57.50' N lat. (Mendocino
Management Area), recreational fishing for California scorpionfish is
open from May 1 through December 31 (i.e., it's closed from January 1
through April 30).
(2) Between 38[deg]57.50' N lat. and 37[deg]11' N lat. (San
Francisco Management Area), recreational fishing for California
scorpionfish is open from April 15 through December 31 (i.e., it's
closed from January 1 through April 14).
(3) Between 37[deg]11' N lat. and 34[deg]27' N lat. (Central
Management Area), recreational fishing for California scorpionfish is
open from April 1 through December 31 (i.e., it's closed from January 1
through March 31).
(4) South of 34[deg]27' N lat. (Southern Management Area),
recreational fishing for California scorpionfish is open from January 1
through December 31.
(B) Bag limits, hook limits. South of 40[deg]10.00' N lat., in
times and areas where the recreational season for California
scorpionfish is open there is a limit of 2 hooks and 1 line, the bag
limit is 5 California scorpionfish per day. California scorpionfish do
not count against the 10 RCG Complex fish per day limit. 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.
* * * * *
(d) Salmon bycatch. Recreational fisheries that are not accounted
for within pre-season salmon modeling may be closed through automatic
action at 660.60(d)(1)(v) and (d)(1)(vi).
[FR Doc. 2018-19460 Filed 9-18-18; 8:45 am]
BILLING CODE 3510-22-P