Notice of Intent To Prepare an Environmental Impact Statement for Minimizing Non-Chinook Salmon Bycatch in the Bering Sea Pollock Fishery in the Bering Sea/Aleutian Islands Fishery Management Plan Area, 44096-44100 [2023-14581]
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are finalized. Future adjustments to the
OPPS conversion factor to offset the
additional non-drug item and service
payments made from CY 2018 through
CY 2022 due to the 340B payment
policy would be discussed in the annual
rulemaking to which the adjustment
would apply. The analyses we have
provided in this section of this proposed
rule, in conjunction with the remainder
of this document, demonstrate that this
proposed rule is consistent with the
regulatory philosophy and principles
identified in Executive Order 12866 as
amended by Executive Order 14094, the
RFA, and section 1102(b) of the Act.
This proposed rule would affect
payments to a small number of small
rural hospitals, as well as other classes
of hospitals, and some effects may be
significant.
In accordance with the provisions of
Executive Order 12866, this regulation
was reviewed by the Office of
Management and Budget.
Chiquita Brooks-LaSure,
Administrator of the Centers for
Medicare & Medicaid Services,
approved this document on June 15,
2023.
List of Subjects in 42 CFR Part 419
Hospitals, Medicare, Reporting and
recordkeeping requirements.
For the reasons set forth in the
preamble, the Centers for Medicare &
Medicaid Services proposes to amend
42 CFR chapter IV as set forth below:
PART 419—PROSPECTIVE PAYMENT
SYSTEMS FOR HOSPITAL
OUTPATIENT DEPARTMENT
SERVICES
1. The authority citation for part 419
continues to read as follows:
■
Authority: 42 U.S.C. 1302, 1395l(t), and
1395hh.
2. Section 419.32 is amended by
revising paragraph (b)(1)(iv)(B)(11) and
adding paragraph (b)(1)(iv)(B)(12) to
read as follows:
■
§ 419.32 Calculation of prospective
payment rates for hospital outpatient
services.
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(iv) * * *
(B) * * *
(11) For calendar year 2020 through
calendar year 2024, a multifactor
productivity adjustment (as determined
by CMS).
(12) Beginning in calendar year 2025,
a multifactor productivity adjustment
(as determined by CMS) and 0.5
percentage point, except that the 0.5
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percentage point reduction shall not
apply to hospital outpatient items and
services, not including separately
payable drugs, furnished by a hospital
with a CMS certification number (CCN)
effective date of January 2, 2018, or
later. This reduction and associated
exception to the reduction will be in
effect until such time that estimated
payment reductions equal $7.8 billion.
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Dated: July 6, 2023.
Xavier Becerra,
Secretary, Department of Health and Human
Services.
[FR Doc. 2023–14623 Filed 7–7–23; 4:15 pm]
BILLING CODE 4120–01–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 679
RTID 0648–XD130
Notice of Intent To Prepare an
Environmental Impact Statement for
Minimizing Non-Chinook Salmon
Bycatch in the Bering Sea Pollock
Fishery in the Bering Sea/Aleutian
Islands Fishery Management Plan Area
National Marine Fisheries
Service (NMFS), Alaska Regional Office
(AKR), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notification; intent to prepare
an environmental impact statement;
request for written comments.
AGENCY:
NMFS, in consultation with
the North Pacific Fishery Management
Council (Council), announces its intent
to prepare an Environmental Impact
Statement (EIS) on management
measures to minimize non-Chinook
salmon bycatch, particularly bycatch of
chum salmon (Oncorhynchus keta) of
western Alaska origin (Western Alaska
chum), in accordance with the National
Environmental Policy Act of 1969
(NEPA). The management measures
analyzed in this EIS would apply
exclusively to participants in the Bering
Sea pollock (Gadus chalcogrammus)
fishery, managed under the Fishery
Management Plan for Groundfish of the
Bering Sea and Aleutian Islands
Management Area (BSAI FMP), and
consistent with the Magnuson-Stevens
Fishery Conservation and Management
Act (Magnuson-Stevens Act), National
Standards, and other applicable law.
The scope of the EIS will be to analyze
the impacts to the human environment
SUMMARY:
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resulting from alternatives for measures
to minimize non-Chinook salmon
bycatch. NMFS will accept written
comments from the public to identify
the issues of concern and assist the
Council and NMFS in determining the
appropriate range of alternatives for the
EIS.
DATES: Written comments will be
accepted through September 15, 2023.
ADDRESSES: You may submit comments
on this document, identified by NOAA–
NMFS–2023–0089, by any of the
following methods:
• Electronic Submission: Submit all
electronic public comments via the
Federal e-Rulemaking Portal. Go to
https://www.regulations.gov and enter
NOAA–NMFS–2023–0089 in the Search
box. Click on the ‘‘Comment’’ icon,
complete the required fields, and enter
or attach your comments.
• Mail: Submit written comments to
Gretchen Harrington, Assistant Regional
Administrator, Sustainable Fisheries
Division, Alaska Region NMFS, Attn:
Susan Meyer. Mail comments to P.O.
Box 21668, Juneau, AK 99802–1668.
Instructions: Comments sent by any
other method, to any other address or
individual, or received after the end of
the comment period, may not be
considered by NMFS. All comments
received are a part of the public record
and will generally be posted for public
viewing on https://www.regulations.gov
without change. All personal identifying
information (e.g., name, address),
confidential business information, or
otherwise sensitive information
submitted voluntarily by the sender will
be publicly accessible. NMFS will
accept anonymous comments (enter ‘‘N/
A’’ in the required fields if you wish to
remain anonymous).
FOR FURTHER INFORMATION CONTACT:
Bridget Mansfield, (907) 586–7228,
Bridget.Mansfield@noaa.gov.
SUPPLEMENTARY INFORMATION:
Authority for Action
Under the Magnuson-Stevens Act, the
United States has exclusive fishery
management authority over all living
marine resources found within the
exclusive economic zone (EEZ) (i.e.,
those waters that are 3 to 200 nautical
miles (approximately 6 to 370
kilometers) from shore). The
management of these marine resources,
with the exception of birds and some
marine mammals, is vested in the
Secretary of Commerce. The Council
shares responsibility for preparing FMPs
for the fisheries that require
conservation and management in the
EEZ off Alaska. Management of the
Federal groundfish fisheries in the BSAI
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is carried out under the BSAI FMP. The
BSAI FMP, its amendments, and
implementing regulations (found at 50
CFR part 679) are developed in
accordance with the requirements of the
Magnuson-Stevens Act and other
applicable Federal laws and executive
orders, notably NEPA and the
Endangered Species Act.
Non-Chinook (Chum) Salmon Bycatch
Management in the BSAI Groundfish
Fisheries
The Magnuson-Stevens Act authorizes
the Council and NMFS to manage
groundfish fisheries in the Alaska EEZ.
Some of these fisheries incidentally
catch salmon as bycatch while targeting
groundfish. The Council has designated
salmon and several other species
(herring, Pacific halibut, steelhead, and
king and Tanner crab) as ‘‘prohibited
species’’ (Section 3.6.1 of the BSAI
FMP). By regulation, the operator of any
vessel fishing for groundfish in the BSAI
must minimize the catch of prohibited
species (§ 679.21(a)(2)(i)). For catch
accounting purposes, NMFS monitors
salmon prohibited species catch (PSC)
as either ‘ ‘‘Chinook (Oncorhynchus
tshawytscha) PSC’’ ’ or ‘ ‘‘non-Chinook
PSC.’’ ’ Sockeye (O. nerka), coho (O.
kisutch), pink (O. gorbuscha), and chum
salmon are included in the non-Chinook
PSC category. However, over 99 percent
of the salmon bycatch in the nonChinook category are chum salmon. PSC
limits are the upper bound of the PSC
allowances apportioned to BSAI
groundfish fisheries as specified
annually under § 679.21. NMFS closes a
fishery to avoid exceeding some
specified PSC limits.
The Council and NMFS have been
actively managing salmon bycatch in
the Bering Sea since the mid-1990s. The
Council’s current salmon bycatch
management program is designed to
minimize salmon bycatch at all levels of
salmon and pollock abundance,
although the PSC limit for Chinook
salmon in the Bering Sea pollock fishery
is reduced in years of low Chinook
salmon abundance (§ 679.21(f)(2)).
Much of the salmon bycatch reduction
focus has been on Chinook salmon,
although salmon bycatch reduction
measures also include chum salmon.
Salmon bycatch reduction actions
previously implemented include the
following measures.
The Chum Salmon Savings Area,
established in 1994 by emergency rule,
was formalized through BSAI FMP
Amendment 35 in 1995 (60 FR 34904,
July 5, 1995). These actions closed the
Chum Salmon Savings Area in the
Bering Sea to all trawling from August
1 through August 31 and stipulated it
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would remain closed through October
14 if the bycatch limit of 42,000 nonChinook salmon was met in the Catcher
Vessel Operational Area (CVOA) after
August 31. The CVOA encompasses the
Chum Salmon Savings Area, effectively
closing both areas to trawling if the limit
was reached.
The voluntary rolling hot spot closure
system (VRHS) was implemented by the
pollock industry for chum salmon in
2001 and Chinook salmon in 2002 to
facilitate sharing real-time salmon
bycatch information to avoid areas with
high Chinook and chum salmon bycatch
rates (i.e., the number of salmon
incidentally caught per metric ton of
pollock).
In 2007, BSAI FMP Amendment 84
implementing regulations addressed
increases in Chinook and chum salmon
bycatch that were occurring despite the
PSC limits in place to trigger closures of
the Chinook and Chum Salmon Savings
Areas (72 FR 61070, October 29, 2007).
These regulations established the
salmon bycatch Intercooperative
Agreement (ICA), which allowed vessels
participating in the Bering Sea pollock
fishery to use their internal cooperative
structure to reduce Chinook and chum
salmon bycatch using the VRHS. Under
Amendment 84 vessels participating in
the VRHS under the ICA were exempt
from the Salmon Savings Area closures.
Amendment 84 also requires the
efficacy of the VRHS program and
bycatch reduction efforts to be reported
to the Council annually.
Prior to Amendment 84’s
implementing regulations, the Council
began to work on a comprehensive
bycatch management package for both
Chinook and chum salmon which
considered updated closure areas and a
range of overall PSC limits by fishery
sector, season, and species. However,
2007 saw the highest historical bycatch
of Chinook salmon coincide with
ongoing observations of and concerns
about declining Chinook stocks of
western Alaska origin. Therefore, the
Council prioritized management
measures for Chinook salmon bycatch,
resulting in BSAI FMP Amendment 91
in 2010 (75 FR 53026, August 30, 2010).
Amendment 91 substantially changed
Chinook salmon bycatch management in
the Bering Sea pollock fishery by
creating two Chinook salmon PSC limits
or ‘‘hard caps.’’ The Chinook salmon
PSC limits were implemented alongside
industry-developed contractual
arrangements called Incentive Plan
Agreements (IPAs). IPAs are designed to
incentivize the pollock industry to
minimize their Chinook salmon bycatch
at all levels of Chinook salmon
abundance. This combined approach
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also provides the pollock industry with
the flexibility to harvest the Bering Sea
pollock Total Allowable Catch (TAC) in
years when encounter rates for Chinook
salmon are higher and salmon are
difficult to avoid on the fishing grounds.
Under Amendment 91, if the pollock
industry developed IPAs, an overall cap
of 60,000 Chinook salmon was
implemented. If the pollock industry
did not develop IPAs, a lower limit of
47,591 Chinook salmon applied fleet
wide. Three IPAs have been in place
since 2010. The overall hard cap is
divided between the A and B pollock
seasons and allocated among the
catcher/processor (CP), mothership,
inshore catcher vessel (CV), and
Community Development Quota (CDQ)
sectors. Amendment 91 also created a
performance standard that required that
each sector not exceed its allocation of
47,591 Chinook salmon in any 3 out of
7 consecutive years.
Salmon bycatch monitoring in the
Bering Sea pollock fishery changed in
2011 to enable Chinook salmon bycatch
accounting, although the measures are
applied to all salmon. Bycatch
monitoring of all salmon species in the
Bering Sea pollock fishery is
accomplished through the following
measures: (1) requirements for 100
percent observer coverage for all vessels
and processing plants; (2) salmon
retention requirements; (3) specific
areas to store and count all salmon,
regardless of species; (4) video
monitoring on at-sea processors; and (5)
electronic reporting of salmon, by
species, by haul (for CPs) or delivery
(for motherships and shoreside
processors). Full retention of all salmon
is required because it is difficult to
differentiate Chinook salmon from other
salmon species, and salmon of all
species are counted using the same
methods. The North Pacific Observer
Program also implemented more robust
genetic sampling, which is required to
achieve the Council’s priority of
minimizing Western Alaska chum
salmon bycatch. Every salmon caught as
bycatch in the Bering Sea pollock
fishery is counted and recorded. Every
10th Chinook salmon and every 30th
chum salmon are sampled by a NMFScertified observer and are used to collect
biological information including length
and tissues used to determine the
genetic stock of origin, among other
data.
Amendment 110 to the BSAI FMP,
implemented in 2016, further refined
salmon bycatch management in the
Bering Sea pollock fishery to improve
the incentives to avoid Chinook and
chum salmon, while providing more
flexibility to the pollock fleet to change
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fishing operations to improve its
opportunity to harvest the pollock TAC
(81 FR 37534, June 10, 2016). Key
elements of Amendment 110 and
implementing regulations that
addressed salmon bycatch included:
• Incorporate chum salmon
avoidance into the IPAs established
under Amendment 91, and remove the
non-Chinook salmon bycatch reduction
ICA previously established under
Amendment 84 to the FMP;
• Modify the requirements for the
content of the IPAs to increase the
incentives for fishermen to avoid
Chinook salmon;
• Change the seasonal
apportionments of the pollock TAC to
allow more pollock to be harvested
earlier in the year when Chinook
salmon PSC use tends to be lower;
• Reduce the Chinook salmon PSC
limit to 45,000 Chinook salmon and
performance standard to 33,318
Chinook salmon in years with low
Chinook salmon abundance in western
Alaska; and
• Improve the monitoring of salmon
bycatch in the pollock fishery.
Amendment 110 further clarified and
strengthened salmon monitoring
regulations implemented under
Amendment 91. Those changes: (1)
revised salmon retention and handling
requirements on catcher vessels; (2)
improved observer data entry and
transmission requirements for catcher
vessels; (3) clarified requirements
applicable to viewing salmon in a
storage container; and (4) clarified
requirements for the removal of salmon
from an observer sampling station at the
end of a haul or delivery.
Proposed Action
The Council is now considering
management measures to further
minimize non-Chinook salmon bycatch
in light of the ongoing declines in chum
salmon run strength across western and
Interior Alaska. Concurrent with the
changes in chum salmon stock
abundance, the Council reviewed
scientific reports outlining the impact of
warming ocean conditions on salmon
mortality at sea and received substantial
public comment from western and
Interior Alaska Tribes, Tribal Consortia,
and subsistence salmon fishermen
describing the importance of chum
salmon for food security, wellbeing, and
the continuation of meaningful cultural
practices and related Traditional
Knowledge (TK) systems. The Council
also received public comments and
annual presentations from IPA
representatives on the industry’s efforts
to minimize their salmon bycatch. As
part of this action, the EIS will analyze
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the extent to which implementing
additional chum salmon bycatch
management measures could have some
positive benefit on the number of chum
salmon that return to western Alaska
rivers. Any additional chum salmon
returning to Alaska river systems
improves the ability to meet the State’s
spawning escapement goals, which is
necessary for the long-term
sustainability of chum salmon.
The Council’s intent for this proposed
action is to minimize the bycatch of
chum salmon, particularly those of
western Alaska origin. The management
measures to be analyzed in this EIS
would apply exclusively to participants
in the Bering Sea pollock fishery
because the majority of non-Chinook
bycatch occurs in the Bering Sea pollock
fishery (∼98%). The EIS will analyze a
range of alternatives considered for the
proposed action to minimize nonChinook salmon bycatch, particularly
the bycatch of Western Alaska chum
salmon, in the Bering Sea pollock
fishery. The chum salmon bycatch
reduction measures under consideration
would augment current bycatch
reduction measures in the Bering Sea
pollock fishery. The BSAI area is
defined at § 679.2 and shown in Figures
1 to 50 CFR part 679.
In June 2023, the Council and NMFS
agreed that NMFS would initiate public
scoping to prepare an EIS for the
proposed action to minimize nonChinook salmon bycatch, particularly
bycatch of Western Alaska chum salmon
in the Bering Sea pollock fishery.
Additional information on the Council’s
proposed action to minimize chum
salmon bycatch is available on the
Council’s website at https://
www.npfmc.org/.
Purpose and Need Statement
In April 2023, the Council adopted
the following Purpose and Need
Statement with additional language
added by NMFS that addresses National
Standard 9:
Salmon are an important fishery
resource throughout Alaska, and chum
salmon that rear in the Bering Sea
support subsistence, commercial, sport,
and recreational fisheries throughout
western and Interior Alaska. Western
and Interior Alaska salmon stocks are
undergoing extreme crises and
collapses, with long-running stock
problems and consecutive years’ failures
to achieve escapement goals, U.S.Canada fish passage treaty requirements,
and subsistence harvest needs in the
Yukon, Kuskokwim, and Norton Sound
regions. These multi-salmon species
declines have created adverse impacts
to culture and food security and have
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resulted in reduced access to traditional
foods and commercial salmon fisheries.
The best available science suggests
that ecosystem and climate changes are
the leading causes of recent chum
salmon run failures; however, nonChinook (primarily chum) salmon are
taken in the Eastern Bering Sea pollock
trawl fishery, which reduces the amount
of salmon that return to western and
Interior Alaska rivers and subsistence
fisheries. It is important to acknowledge
and understand all sources of chum
mortality and the cumulative impact of
various fishing activities. In light of the
critical importance of chum salmon to
western Alaska communities and
ecosystems, the Council is considering
additional measures to further minimize
Western Alaska chum bycatch in the
pollock fishery.
The purpose of this proposed action
is to develop actions to minimize
bycatch of Western Alaska chum salmon
in the Eastern Bering Sea pollock fishery
consistent with the Magnuson-Stevens
Act, National Standards, and other
applicable law. In particular, National
Standard 9 provides that conservation
and management measures shall, to the
extent practicable, (a) minimize bycatch
and (b) to the extent bycatch cannot be
avoided, minimize the mortality of such
bycatch. Consistent, annual genetics
stock composition information indicates
that the majority of non-Chinook
bycatch in the pollock fishery is of
Russian/Asian hatchery origin;
therefore, alternatives should structure
non-Chinook bycatch management
measures around improving
performance in avoiding Western
Alaska chum salmon specifically.
The Council intends to consider
establishing additional regulatory nonChinook bycatch management measures
that reduce Western Alaska chum
bycatch and meet the following
objectives; (1) provide additional
opportunities for the pollock trawl fleet
to improve performance in avoiding
non-Chinook salmon, while maintaining
the priority of the objectives of the
Amendment 91 and Amendment 110
Chinook salmon bycatch avoidance
program; (2) meet and balance the
requirements of the Magnuson-Stevens
Act, particularly to minimize salmon
bycatch to the extent practicable under
National Standard 9; (3) include the best
scientific information available
including Local Knowledge and TK as
required by National Standard 2; (4)
take into account the importance of
fishery resources to fishing communities
including those that are dependent on
Bering Sea pollock and subsistence
salmon fisheries as required under
National Standard 8; and (5) achieve
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optimum yield in the BSAI groundfish
fisheries on a continuing basis, in the
groundfish fisheries as required under
National Standard 1.
Alternatives and Options for NonChinook (Chum) Salmon Bycatch
Reduction
NMFS, in coordination with the
Council, will evaluate a range of
alternative methods to minimize nonChinook salmon bycatch, with a
primary focus on reducing Western
Alaska chum salmon bycatch in the
Bering Sea pollock fishery in
accordance with the Magnuson-Stevens
Act. NMFS and the Council recognize
that implementation of additional
measures to minimize chum PSC could
change aspects of the existing
management measures for non-Chinook
PSC in the Bering Sea pollock fishery.
Possible alternatives for minimizing
non-Chinook bycatch in the Bering Sea
pollock fishery could be constructed
from one or more of the following draft
alternatives and options developed by
the Council, in addition to those
developed through the public scoping
and future Council processes:
Alternative 1: Status Quo, No Action
Alternative 1 is the current
management of the Bering Sea pollock
fishery with the measures to minimize
non-Chinook salmon PSC under
Amendment 110, as described above,
and the associated monitoring and
genetic data collection and analysis.
All action alternatives apply to the
entire Bering Sea pollock B season, the
season in which chum salmon are taken
as bycatch.
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Alternative 2: Overall PSC Limit for
Chum Salmon
Option 1: Chum salmon PSC limit (a
range to be informed by PSC data).
PSC limits are apportioned among
CDQ, CP, mothership, and inshore
sectors based on historical total bycatch
by sector. The inshore limit is further
apportioned among the inshore
cooperatives. The CDQ limit is further
apportioned among the CDQ groups.
Reaching a PSC limit closes the pollock
fishery sector to which the PSC limit
applies.
Option 2: Weighted, step-down PSC
limit triggered by a three-river chum
index (Kwiniuk (or index developed for
Norton Sound area), Yukon,
Kuskokwim) that is linked to prior
years’ chum abundance/amount
necessary for subsistence (ANS)/
escapement and weighted to account for
variance in stock sizes across river
systems.
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PSC limits would be triggered and in
effect when one or more Western Alaska
chum index areas fails to meet index
thresholds. As more areas fail to meet
index thresholds, chum PSC limits
would step-down and become more
restrictive. PSC limits are apportioned
among CDQ, CP, mothership and
inshore sectors. The inshore limit is
further apportioned among the inshore
cooperatives. The CDQ limit is further
apportioned among the CDQ groups.
Reaching a PSC limit closes the pollock
fishery sector to which the PSC limit
applies.
Alternative 3: PSC Limit for Western
Alaska Chum Salmon
Option 1: Western Alaska chum
salmon PSC limit (range to be informed
by PSC data).
PSC limits are apportioned among
CDQ, CP, mothership, and inshore
sectors based on historical total bycatch
by sector. The inshore limit is further
apportioned among the inshore
cooperatives. The CDQ limit is further
apportioned among the CDQ groups.
Reaching a PSC limit closes the pollock
fishery sector to which the PSC limit
applies.
Option 2: Weighted, step-down
Western Alaska chum PSC limit
triggered by a three-river chum index
(Kwiniuk (or index developed for
Norton Sound area), Yukon,
Kuskokwim) that is linked to prior
years’ chum abundance/ANS/
escapement and weighted to account for
variance in stock sizes across river
systems.
PSC limits would be triggered and in
effect when one or more Western Alaska
chum index areas fails to meet index
thresholds. As more areas fail to meet
index thresholds, chum PSC limits
would step-down and become more
restrictive. PSC limits are apportioned
among CDQ, CP, mothership, and
inshore sectors. The inshore limit is
further apportioned among the inshore
cooperatives. The CDQ limit is further
apportioned among the CDQ groups.
Reaching a PSC limit closes the pollock
fishery sector to which the PSC limit
applies.
Alternative 4: Additional Regulatory
Requirements for IPAs To Be Managed
by Either NMFS or Within the IPAs
Option 1: Require a chum salmon
reduction plan agreement to prioritize
avoidance in Genetic Cluster Areas 1
and 2 for a specified amount of time
based on two triggers: (1) exceeding an
established chum salmon incidental
catch rate; and (2) exceeding a historical
genetic composition (proportion) of
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Western Alaska chum salmon to nonWestern Alaska chum salmon.
Option 2: Additional regulatory
provisions requiring IPAs to utilize the
most refined genetic information
available to further prioritize avoidance
of areas and times with higher
proportions of Western Alaska and
Upper/Middle Yukon chum stocks.
Issues To Be Analyzed
The EIS will analyze these
alternatives, and any additional
alternatives developed through the
scoping and Council processes, and
their likely impacts on non-Chinook
salmon stocks, elements of associated
marine resources, and participants in
the directed pollock fishery. The EIS
also will analyze the likely impacts of
such additional non-Chinook salmon
PSC limits on related Chinook salmon
stocks and on participants in
subsistence salmon fisheries in the area.
When the Council adopted a Purpose
and Need statement in April 2023, the
Council asked for a preliminary
analysis, which will be presented at the
October 2023 Council meeting, along
with a summary of scoping comments
received in response to this notice, to
provide information to inform a
reasonable range of PSC limits and an
index associated with Western Alaska
chum salmon stock status under the
action alternatives. The preliminary
analysis will address:
• Non-Chinook PSC data by year from
2011 through 2022; 3-, 5-, 10-year
average non-Chinook PSC levels from
2011 through 2022; and potential ranges
for average PSC levels during warm/
cold years from 2011 through 2022.
• Whether the identified areas
(Kwiniuk (or Norton Sound area),
Kuskokwim, Yukon) are appropriate as
indices to determine Western Alaska
chum salmon abundance and whether
there are data to support consistent use
of each area in an index.
• Which criteria should be used to
define low index abundance in each
area (i.e., a number of chum defining
poor abundance) for each area?
Examples:
—abundance (e.g., a percentile of
historical abundance)
—subsistence harvest performance (e.g.,
subsistence harvest in relation to
historical subsistence harvest and/or
ANS)
—achievement of escapement goals
(e.g., a percentage of total escapement
goals met or exceeded)
• The feasibility of NMFS
implementing a Western Alaska chum
PSC limit under Alternative 3. For
example, can NMFS apply the Western
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Alaska chum stock proportion available
in spring 2025 to total chum PSC at the
end of year 2024 to trigger management
measures in B season 2025? Or a
measure whereby Western Alaska chum
PSC limit is reduced if exceeded for a
maximum number of consecutive years
(e.g., 2 out of 5 years or 3 out of 7
years)?
• Additional information necessary to
analyze IPAs such as the base rate for
triggering action, e.g., the proportion of
Western Alaska and non-Western
Alaska chum salmon for the second
trigger in Alternative 4, Option 1.
• A summary of research and TK that
can be gathered to understand all causes
of the population decline.
ddrumheller on DSK120RN23PROD with PROPOSALS1
Public Involvement
Scoping is an early and open process
for determining the scope of issues to be
addressed in an EIS and for identifying
the significant issues related to the
proposed action (40 CFR 1501.9). An
EIS is a detailed statement on a
proposed agency action, but it does not
mandate particular results or
substantive outcomes as the purpose
and function of NEPA is satisfied if the
agency considered relevant
environmental information and the
VerDate Sep<11>2014
16:38 Jul 10, 2023
Jkt 259001
public has been informed regarding the
decision-making process (40 CFR
1500.1(a)). A principal objective of the
scoping and public involvement process
is to identify a range of reasonable
management alternatives that, with
adequate analysis in an EIS, will
delineate critical issues and provide a
clear basis for distinguishing among
those alternatives and informing the
selection of a preferred alternative.
Through this notice, NMFS is notifying
the public that an EIS and a decisionmaking process for this proposed action
have been initiated so that interested or
affected people may participate and
contribute to the final decision.
NMFS is seeking written public
comments on the scope of issues,
including potential impacts, and
alternatives that should be considered to
minimize non-Chinook salmon bycatch,
particularly the bycatch of Western
Alaska chum salmon, in the Bering Sea
pollock fishery. Written comments
should be as specific as possible to be
the most helpful. Written comments
received during the scoping process,
including the names and addresses of
those submitting them, will be
considered part of the public record of
this proposal and will be available for
PO 00000
Frm 00036
Fmt 4702
Sfmt 9990
public inspection. Written comments
will be accepted at the address above
(see ADDRESSES). Please visit the NMFS
Alaska Region website at https://
www.alaskafisheries.noaa.gov for more
information on salmon bycatch
management in Alaska.
Subsequent to the formal scoping
period for written comments, which this
notice announces, the public is invited
to participate and provide additional
relevant input at Council meetings,
where the latest scientific information
regarding chum bycatch in the Bering
Sea pollock fishery is reviewed and
alternatives will be developed and
evaluated for this EIS. Notice of future
Council meetings will be published in
the Federal Register and on the internet
at https://www.npfmc.org/. Please visit
this website for information and
guidance on participating in Council
meetings.
Authority: 16 U.S.C. 1801 et seq.
Dated July 5, 2023.
Jennifer M. Wallace,
Acting Director, Office of Sustainable
Fisheries, National Marine Fisheries Service.
[FR Doc. 2023–14581 Filed 7–10–23; 8:45 am]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 88, Number 131 (Tuesday, July 11, 2023)]
[Proposed Rules]
[Pages 44096-44100]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2023-14581]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 679
RTID 0648-XD130
Notice of Intent To Prepare an Environmental Impact Statement for
Minimizing Non-Chinook Salmon Bycatch in the Bering Sea Pollock Fishery
in the Bering Sea/Aleutian Islands Fishery Management Plan Area
AGENCY: National Marine Fisheries Service (NMFS), Alaska Regional
Office (AKR), National Oceanic and Atmospheric Administration (NOAA),
Commerce.
ACTION: Notification; intent to prepare an environmental impact
statement; request for written comments.
-----------------------------------------------------------------------
SUMMARY: NMFS, in consultation with the North Pacific Fishery
Management Council (Council), announces its intent to prepare an
Environmental Impact Statement (EIS) on management measures to minimize
non-Chinook salmon bycatch, particularly bycatch of chum salmon
(Oncorhynchus keta) of western Alaska origin (Western Alaska chum), in
accordance with the National Environmental Policy Act of 1969 (NEPA).
The management measures analyzed in this EIS would apply exclusively to
participants in the Bering Sea pollock (Gadus chalcogrammus) fishery,
managed under the Fishery Management Plan for Groundfish of the Bering
Sea and Aleutian Islands Management Area (BSAI FMP), and consistent
with the Magnuson-Stevens Fishery Conservation and Management Act
(Magnuson-Stevens Act), National Standards, and other applicable law.
The scope of the EIS will be to analyze the impacts to the human
environment resulting from alternatives for measures to minimize non-
Chinook salmon bycatch. NMFS will accept written comments from the
public to identify the issues of concern and assist the Council and
NMFS in determining the appropriate range of alternatives for the EIS.
DATES: Written comments will be accepted through September 15, 2023.
ADDRESSES: You may submit comments on this document, identified by
NOAA-NMFS-2023-0089, by any of the following methods:
Electronic Submission: Submit all electronic public
comments via the Federal e-Rulemaking Portal. Go to https://www.regulations.gov and enter NOAA-NMFS-2023-0089 in the Search box.
Click on the ``Comment'' icon, complete the required fields, and enter
or attach your comments.
Mail: Submit written comments to Gretchen Harrington,
Assistant Regional Administrator, Sustainable Fisheries Division,
Alaska Region NMFS, Attn: Susan Meyer. Mail comments to P.O. Box 21668,
Juneau, AK 99802-1668.
Instructions: Comments sent by any other method, to any other
address or individual, or received after the end of the comment period,
may not be considered by NMFS. All comments received are a part of the
public record and will generally be posted for public viewing on
https://www.regulations.gov without change. All personal identifying
information (e.g., name, address), confidential business information,
or otherwise sensitive information submitted voluntarily by the sender
will be publicly accessible. NMFS will accept anonymous comments (enter
``N/A'' in the required fields if you wish to remain anonymous).
FOR FURTHER INFORMATION CONTACT: Bridget Mansfield, (907) 586-7228,
[email protected].
SUPPLEMENTARY INFORMATION:
Authority for Action
Under the Magnuson-Stevens Act, the United States has exclusive
fishery management authority over all living marine resources found
within the exclusive economic zone (EEZ) (i.e., those waters that are 3
to 200 nautical miles (approximately 6 to 370 kilometers) from shore).
The management of these marine resources, with the exception of birds
and some marine mammals, is vested in the Secretary of Commerce. The
Council shares responsibility for preparing FMPs for the fisheries that
require conservation and management in the EEZ off Alaska. Management
of the Federal groundfish fisheries in the BSAI
[[Page 44097]]
is carried out under the BSAI FMP. The BSAI FMP, its amendments, and
implementing regulations (found at 50 CFR part 679) are developed in
accordance with the requirements of the Magnuson-Stevens Act and other
applicable Federal laws and executive orders, notably NEPA and the
Endangered Species Act.
Non-Chinook (Chum) Salmon Bycatch Management in the BSAI Groundfish
Fisheries
The Magnuson-Stevens Act authorizes the Council and NMFS to manage
groundfish fisheries in the Alaska EEZ. Some of these fisheries
incidentally catch salmon as bycatch while targeting groundfish. The
Council has designated salmon and several other species (herring,
Pacific halibut, steelhead, and king and Tanner crab) as ``prohibited
species'' (Section 3.6.1 of the BSAI FMP). By regulation, the operator
of any vessel fishing for groundfish in the BSAI must minimize the
catch of prohibited species (Sec. 679.21(a)(2)(i)). For catch
accounting purposes, NMFS monitors salmon prohibited species catch
(PSC) as either ` ``Chinook (Oncorhynchus tshawytscha) PSC'' ' or `
``non-Chinook PSC.'' ' Sockeye (O. nerka), coho (O. kisutch), pink (O.
gorbuscha), and chum salmon are included in the non-Chinook PSC
category. However, over 99 percent of the salmon bycatch in the non-
Chinook category are chum salmon. PSC limits are the upper bound of the
PSC allowances apportioned to BSAI groundfish fisheries as specified
annually under Sec. 679.21. NMFS closes a fishery to avoid exceeding
some specified PSC limits.
The Council and NMFS have been actively managing salmon bycatch in
the Bering Sea since the mid-1990s. The Council's current salmon
bycatch management program is designed to minimize salmon bycatch at
all levels of salmon and pollock abundance, although the PSC limit for
Chinook salmon in the Bering Sea pollock fishery is reduced in years of
low Chinook salmon abundance (Sec. 679.21(f)(2)). Much of the salmon
bycatch reduction focus has been on Chinook salmon, although salmon
bycatch reduction measures also include chum salmon. Salmon bycatch
reduction actions previously implemented include the following
measures.
The Chum Salmon Savings Area, established in 1994 by emergency
rule, was formalized through BSAI FMP Amendment 35 in 1995 (60 FR
34904, July 5, 1995). These actions closed the Chum Salmon Savings Area
in the Bering Sea to all trawling from August 1 through August 31 and
stipulated it would remain closed through October 14 if the bycatch
limit of 42,000 non-Chinook salmon was met in the Catcher Vessel
Operational Area (CVOA) after August 31. The CVOA encompasses the Chum
Salmon Savings Area, effectively closing both areas to trawling if the
limit was reached.
The voluntary rolling hot spot closure system (VRHS) was
implemented by the pollock industry for chum salmon in 2001 and Chinook
salmon in 2002 to facilitate sharing real-time salmon bycatch
information to avoid areas with high Chinook and chum salmon bycatch
rates (i.e., the number of salmon incidentally caught per metric ton of
pollock).
In 2007, BSAI FMP Amendment 84 implementing regulations addressed
increases in Chinook and chum salmon bycatch that were occurring
despite the PSC limits in place to trigger closures of the Chinook and
Chum Salmon Savings Areas (72 FR 61070, October 29, 2007). These
regulations established the salmon bycatch Intercooperative Agreement
(ICA), which allowed vessels participating in the Bering Sea pollock
fishery to use their internal cooperative structure to reduce Chinook
and chum salmon bycatch using the VRHS. Under Amendment 84 vessels
participating in the VRHS under the ICA were exempt from the Salmon
Savings Area closures. Amendment 84 also requires the efficacy of the
VRHS program and bycatch reduction efforts to be reported to the
Council annually.
Prior to Amendment 84's implementing regulations, the Council began
to work on a comprehensive bycatch management package for both Chinook
and chum salmon which considered updated closure areas and a range of
overall PSC limits by fishery sector, season, and species. However,
2007 saw the highest historical bycatch of Chinook salmon coincide with
ongoing observations of and concerns about declining Chinook stocks of
western Alaska origin. Therefore, the Council prioritized management
measures for Chinook salmon bycatch, resulting in BSAI FMP Amendment 91
in 2010 (75 FR 53026, August 30, 2010).
Amendment 91 substantially changed Chinook salmon bycatch
management in the Bering Sea pollock fishery by creating two Chinook
salmon PSC limits or ``hard caps.'' The Chinook salmon PSC limits were
implemented alongside industry-developed contractual arrangements
called Incentive Plan Agreements (IPAs). IPAs are designed to
incentivize the pollock industry to minimize their Chinook salmon
bycatch at all levels of Chinook salmon abundance. This combined
approach also provides the pollock industry with the flexibility to
harvest the Bering Sea pollock Total Allowable Catch (TAC) in years
when encounter rates for Chinook salmon are higher and salmon are
difficult to avoid on the fishing grounds. Under Amendment 91, if the
pollock industry developed IPAs, an overall cap of 60,000 Chinook
salmon was implemented. If the pollock industry did not develop IPAs, a
lower limit of 47,591 Chinook salmon applied fleet wide. Three IPAs
have been in place since 2010. The overall hard cap is divided between
the A and B pollock seasons and allocated among the catcher/processor
(CP), mothership, inshore catcher vessel (CV), and Community
Development Quota (CDQ) sectors. Amendment 91 also created a
performance standard that required that each sector not exceed its
allocation of 47,591 Chinook salmon in any 3 out of 7 consecutive
years.
Salmon bycatch monitoring in the Bering Sea pollock fishery changed
in 2011 to enable Chinook salmon bycatch accounting, although the
measures are applied to all salmon. Bycatch monitoring of all salmon
species in the Bering Sea pollock fishery is accomplished through the
following measures: (1) requirements for 100 percent observer coverage
for all vessels and processing plants; (2) salmon retention
requirements; (3) specific areas to store and count all salmon,
regardless of species; (4) video monitoring on at-sea processors; and
(5) electronic reporting of salmon, by species, by haul (for CPs) or
delivery (for motherships and shoreside processors). Full retention of
all salmon is required because it is difficult to differentiate Chinook
salmon from other salmon species, and salmon of all species are counted
using the same methods. The North Pacific Observer Program also
implemented more robust genetic sampling, which is required to achieve
the Council's priority of minimizing Western Alaska chum salmon
bycatch. Every salmon caught as bycatch in the Bering Sea pollock
fishery is counted and recorded. Every 10th Chinook salmon and every
30th chum salmon are sampled by a NMFS-certified observer and are used
to collect biological information including length and tissues used to
determine the genetic stock of origin, among other data.
Amendment 110 to the BSAI FMP, implemented in 2016, further refined
salmon bycatch management in the Bering Sea pollock fishery to improve
the incentives to avoid Chinook and chum salmon, while providing more
flexibility to the pollock fleet to change
[[Page 44098]]
fishing operations to improve its opportunity to harvest the pollock
TAC (81 FR 37534, June 10, 2016). Key elements of Amendment 110 and
implementing regulations that addressed salmon bycatch included:
Incorporate chum salmon avoidance into the IPAs
established under Amendment 91, and remove the non-Chinook salmon
bycatch reduction ICA previously established under Amendment 84 to the
FMP;
Modify the requirements for the content of the IPAs to
increase the incentives for fishermen to avoid Chinook salmon;
Change the seasonal apportionments of the pollock TAC to
allow more pollock to be harvested earlier in the year when Chinook
salmon PSC use tends to be lower;
Reduce the Chinook salmon PSC limit to 45,000 Chinook
salmon and performance standard to 33,318 Chinook salmon in years with
low Chinook salmon abundance in western Alaska; and
Improve the monitoring of salmon bycatch in the pollock
fishery.
Amendment 110 further clarified and strengthened salmon monitoring
regulations implemented under Amendment 91. Those changes: (1) revised
salmon retention and handling requirements on catcher vessels; (2)
improved observer data entry and transmission requirements for catcher
vessels; (3) clarified requirements applicable to viewing salmon in a
storage container; and (4) clarified requirements for the removal of
salmon from an observer sampling station at the end of a haul or
delivery.
Proposed Action
The Council is now considering management measures to further
minimize non-Chinook salmon bycatch in light of the ongoing declines in
chum salmon run strength across western and Interior Alaska. Concurrent
with the changes in chum salmon stock abundance, the Council reviewed
scientific reports outlining the impact of warming ocean conditions on
salmon mortality at sea and received substantial public comment from
western and Interior Alaska Tribes, Tribal Consortia, and subsistence
salmon fishermen describing the importance of chum salmon for food
security, wellbeing, and the continuation of meaningful cultural
practices and related Traditional Knowledge (TK) systems. The Council
also received public comments and annual presentations from IPA
representatives on the industry's efforts to minimize their salmon
bycatch. As part of this action, the EIS will analyze the extent to
which implementing additional chum salmon bycatch management measures
could have some positive benefit on the number of chum salmon that
return to western Alaska rivers. Any additional chum salmon returning
to Alaska river systems improves the ability to meet the State's
spawning escapement goals, which is necessary for the long-term
sustainability of chum salmon.
The Council's intent for this proposed action is to minimize the
bycatch of chum salmon, particularly those of western Alaska origin.
The management measures to be analyzed in this EIS would apply
exclusively to participants in the Bering Sea pollock fishery because
the majority of non-Chinook bycatch occurs in the Bering Sea pollock
fishery (~98%). The EIS will analyze a range of alternatives considered
for the proposed action to minimize non-Chinook salmon bycatch,
particularly the bycatch of Western Alaska chum salmon, in the Bering
Sea pollock fishery. The chum salmon bycatch reduction measures under
consideration would augment current bycatch reduction measures in the
Bering Sea pollock fishery. The BSAI area is defined at Sec. 679.2 and
shown in Figures 1 to 50 CFR part 679.
In June 2023, the Council and NMFS agreed that NMFS would initiate
public scoping to prepare an EIS for the proposed action to minimize
non-Chinook salmon bycatch, particularly bycatch of Western Alaska chum
salmon in the Bering Sea pollock fishery. Additional information on the
Council's proposed action to minimize chum salmon bycatch is available
on the Council's website at https://www.npfmc.org/.
Purpose and Need Statement
In April 2023, the Council adopted the following Purpose and Need
Statement with additional language added by NMFS that addresses
National Standard 9:
Salmon are an important fishery resource throughout Alaska, and
chum salmon that rear in the Bering Sea support subsistence,
commercial, sport, and recreational fisheries throughout western and
Interior Alaska. Western and Interior Alaska salmon stocks are
undergoing extreme crises and collapses, with long-running stock
problems and consecutive years' failures to achieve escapement goals,
U.S.-Canada fish passage treaty requirements, and subsistence harvest
needs in the Yukon, Kuskokwim, and Norton Sound regions. These multi-
salmon species declines have created adverse impacts to culture and
food security and have resulted in reduced access to traditional foods
and commercial salmon fisheries.
The best available science suggests that ecosystem and climate
changes are the leading causes of recent chum salmon run failures;
however, non-Chinook (primarily chum) salmon are taken in the Eastern
Bering Sea pollock trawl fishery, which reduces the amount of salmon
that return to western and Interior Alaska rivers and subsistence
fisheries. It is important to acknowledge and understand all sources of
chum mortality and the cumulative impact of various fishing activities.
In light of the critical importance of chum salmon to western Alaska
communities and ecosystems, the Council is considering additional
measures to further minimize Western Alaska chum bycatch in the pollock
fishery.
The purpose of this proposed action is to develop actions to
minimize bycatch of Western Alaska chum salmon in the Eastern Bering
Sea pollock fishery consistent with the Magnuson-Stevens Act, National
Standards, and other applicable law. In particular, National Standard 9
provides that conservation and management measures shall, to the extent
practicable, (a) minimize bycatch and (b) to the extent bycatch cannot
be avoided, minimize the mortality of such bycatch. Consistent, annual
genetics stock composition information indicates that the majority of
non-Chinook bycatch in the pollock fishery is of Russian/Asian hatchery
origin; therefore, alternatives should structure non-Chinook bycatch
management measures around improving performance in avoiding Western
Alaska chum salmon specifically.
The Council intends to consider establishing additional regulatory
non-Chinook bycatch management measures that reduce Western Alaska chum
bycatch and meet the following objectives; (1) provide additional
opportunities for the pollock trawl fleet to improve performance in
avoiding non-Chinook salmon, while maintaining the priority of the
objectives of the Amendment 91 and Amendment 110 Chinook salmon bycatch
avoidance program; (2) meet and balance the requirements of the
Magnuson-Stevens Act, particularly to minimize salmon bycatch to the
extent practicable under National Standard 9; (3) include the best
scientific information available including Local Knowledge and TK as
required by National Standard 2; (4) take into account the importance
of fishery resources to fishing communities including those that are
dependent on Bering Sea pollock and subsistence salmon fisheries as
required under National Standard 8; and (5) achieve
[[Page 44099]]
optimum yield in the BSAI groundfish fisheries on a continuing basis,
in the groundfish fisheries as required under National Standard 1.
Alternatives and Options for Non-Chinook (Chum) Salmon Bycatch
Reduction
NMFS, in coordination with the Council, will evaluate a range of
alternative methods to minimize non-Chinook salmon bycatch, with a
primary focus on reducing Western Alaska chum salmon bycatch in the
Bering Sea pollock fishery in accordance with the Magnuson-Stevens Act.
NMFS and the Council recognize that implementation of additional
measures to minimize chum PSC could change aspects of the existing
management measures for non-Chinook PSC in the Bering Sea pollock
fishery.
Possible alternatives for minimizing non-Chinook bycatch in the
Bering Sea pollock fishery could be constructed from one or more of the
following draft alternatives and options developed by the Council, in
addition to those developed through the public scoping and future
Council processes:
Alternative 1: Status Quo, No Action
Alternative 1 is the current management of the Bering Sea pollock
fishery with the measures to minimize non-Chinook salmon PSC under
Amendment 110, as described above, and the associated monitoring and
genetic data collection and analysis.
All action alternatives apply to the entire Bering Sea pollock B
season, the season in which chum salmon are taken as bycatch.
Alternative 2: Overall PSC Limit for Chum Salmon
Option 1: Chum salmon PSC limit (a range to be informed by PSC
data).
PSC limits are apportioned among CDQ, CP, mothership, and inshore
sectors based on historical total bycatch by sector. The inshore limit
is further apportioned among the inshore cooperatives. The CDQ limit is
further apportioned among the CDQ groups. Reaching a PSC limit closes
the pollock fishery sector to which the PSC limit applies.
Option 2: Weighted, step-down PSC limit triggered by a three-river
chum index (Kwiniuk (or index developed for Norton Sound area), Yukon,
Kuskokwim) that is linked to prior years' chum abundance/amount
necessary for subsistence (ANS)/escapement and weighted to account for
variance in stock sizes across river systems.
PSC limits would be triggered and in effect when one or more
Western Alaska chum index areas fails to meet index thresholds. As more
areas fail to meet index thresholds, chum PSC limits would step-down
and become more restrictive. PSC limits are apportioned among CDQ, CP,
mothership and inshore sectors. The inshore limit is further
apportioned among the inshore cooperatives. The CDQ limit is further
apportioned among the CDQ groups. Reaching a PSC limit closes the
pollock fishery sector to which the PSC limit applies.
Alternative 3: PSC Limit for Western Alaska Chum Salmon
Option 1: Western Alaska chum salmon PSC limit (range to be
informed by PSC data).
PSC limits are apportioned among CDQ, CP, mothership, and inshore
sectors based on historical total bycatch by sector. The inshore limit
is further apportioned among the inshore cooperatives. The CDQ limit is
further apportioned among the CDQ groups. Reaching a PSC limit closes
the pollock fishery sector to which the PSC limit applies.
Option 2: Weighted, step-down Western Alaska chum PSC limit
triggered by a three-river chum index (Kwiniuk (or index developed for
Norton Sound area), Yukon, Kuskokwim) that is linked to prior years'
chum abundance/ANS/escapement and weighted to account for variance in
stock sizes across river systems.
PSC limits would be triggered and in effect when one or more
Western Alaska chum index areas fails to meet index thresholds. As more
areas fail to meet index thresholds, chum PSC limits would step-down
and become more restrictive. PSC limits are apportioned among CDQ, CP,
mothership, and inshore sectors. The inshore limit is further
apportioned among the inshore cooperatives. The CDQ limit is further
apportioned among the CDQ groups. Reaching a PSC limit closes the
pollock fishery sector to which the PSC limit applies.
Alternative 4: Additional Regulatory Requirements for IPAs To Be
Managed by Either NMFS or Within the IPAs
Option 1: Require a chum salmon reduction plan agreement to
prioritize avoidance in Genetic Cluster Areas 1 and 2 for a specified
amount of time based on two triggers: (1) exceeding an established chum
salmon incidental catch rate; and (2) exceeding a historical genetic
composition (proportion) of Western Alaska chum salmon to non-Western
Alaska chum salmon.
Option 2: Additional regulatory provisions requiring IPAs to
utilize the most refined genetic information available to further
prioritize avoidance of areas and times with higher proportions of
Western Alaska and Upper/Middle Yukon chum stocks.
Issues To Be Analyzed
The EIS will analyze these alternatives, and any additional
alternatives developed through the scoping and Council processes, and
their likely impacts on non-Chinook salmon stocks, elements of
associated marine resources, and participants in the directed pollock
fishery. The EIS also will analyze the likely impacts of such
additional non-Chinook salmon PSC limits on related Chinook salmon
stocks and on participants in subsistence salmon fisheries in the area.
When the Council adopted a Purpose and Need statement in April
2023, the Council asked for a preliminary analysis, which will be
presented at the October 2023 Council meeting, along with a summary of
scoping comments received in response to this notice, to provide
information to inform a reasonable range of PSC limits and an index
associated with Western Alaska chum salmon stock status under the
action alternatives. The preliminary analysis will address:
Non-Chinook PSC data by year from 2011 through 2022; 3-,
5-, 10-year average non-Chinook PSC levels from 2011 through 2022; and
potential ranges for average PSC levels during warm/cold years from
2011 through 2022.
Whether the identified areas (Kwiniuk (or Norton Sound
area), Kuskokwim, Yukon) are appropriate as indices to determine
Western Alaska chum salmon abundance and whether there are data to
support consistent use of each area in an index.
Which criteria should be used to define low index
abundance in each area (i.e., a number of chum defining poor abundance)
for each area? Examples:
--abundance (e.g., a percentile of historical abundance)
--subsistence harvest performance (e.g., subsistence harvest in
relation to historical subsistence harvest and/or ANS)
--achievement of escapement goals (e.g., a percentage of total
escapement goals met or exceeded)
The feasibility of NMFS implementing a Western Alaska chum
PSC limit under Alternative 3. For example, can NMFS apply the Western
[[Page 44100]]
Alaska chum stock proportion available in spring 2025 to total chum PSC
at the end of year 2024 to trigger management measures in B season
2025? Or a measure whereby Western Alaska chum PSC limit is reduced if
exceeded for a maximum number of consecutive years (e.g., 2 out of 5
years or 3 out of 7 years)?
Additional information necessary to analyze IPAs such as
the base rate for triggering action, e.g., the proportion of Western
Alaska and non-Western Alaska chum salmon for the second trigger in
Alternative 4, Option 1.
A summary of research and TK that can be gathered to
understand all causes of the population decline.
Public Involvement
Scoping is an early and open process for determining the scope of
issues to be addressed in an EIS and for identifying the significant
issues related to the proposed action (40 CFR 1501.9). An EIS is a
detailed statement on a proposed agency action, but it does not mandate
particular results or substantive outcomes as the purpose and function
of NEPA is satisfied if the agency considered relevant environmental
information and the public has been informed regarding the decision-
making process (40 CFR 1500.1(a)). A principal objective of the scoping
and public involvement process is to identify a range of reasonable
management alternatives that, with adequate analysis in an EIS, will
delineate critical issues and provide a clear basis for distinguishing
among those alternatives and informing the selection of a preferred
alternative. Through this notice, NMFS is notifying the public that an
EIS and a decision-making process for this proposed action have been
initiated so that interested or affected people may participate and
contribute to the final decision.
NMFS is seeking written public comments on the scope of issues,
including potential impacts, and alternatives that should be considered
to minimize non-Chinook salmon bycatch, particularly the bycatch of
Western Alaska chum salmon, in the Bering Sea pollock fishery. Written
comments should be as specific as possible to be the most helpful.
Written comments received during the scoping process, including the
names and addresses of those submitting them, will be considered part
of the public record of this proposal and will be available for public
inspection. Written comments will be accepted at the address above (see
ADDRESSES). Please visit the NMFS Alaska Region website at https://www.alaskafisheries.noaa.gov for more information on salmon bycatch
management in Alaska.
Subsequent to the formal scoping period for written comments, which
this notice announces, the public is invited to participate and provide
additional relevant input at Council meetings, where the latest
scientific information regarding chum bycatch in the Bering Sea pollock
fishery is reviewed and alternatives will be developed and evaluated
for this EIS. Notice of future Council meetings will be published in
the Federal Register and on the internet at https://www.npfmc.org/.
Please visit this website for information and guidance on participating
in Council meetings.
Authority: 16 U.S.C. 1801 et seq.
Dated July 5, 2023.
Jennifer M. Wallace,
Acting Director, Office of Sustainable Fisheries, National Marine
Fisheries Service.
[FR Doc. 2023-14581 Filed 7-10-23; 8:45 am]
BILLING CODE 3510-22-P