Magnuson-Stevens Act Provisions; Annual Catch Limits; National Standard Guidelines, 32526-32547 [08-1328]
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Federal Register / Vol. 73, No. 111 / Monday, June 9, 2008 / Proposed Rules
and commercial information, we solicit
comment from the public, other
governmental agencies, the scientific
community, industry, and any other
interested parties. Title 50, CFR
424.16(c)(3) requires the Secretary of
Commerce to promptly hold at least one
public hearing if any person requests
one within 45 days of publication of a
proposed regulation to change the listed
status of a species under the ESA.
Requests for public hearing must be
made in writing (see DATES and
ADDRESSES). Such hearings provide the
opportunity for interested individuals
and parties to give comments, exchange
information and opinions, and engage in
a constructive dialogue concerning this
proposed rule. We encourage the
public’s involvement in such ESA
matters.
Classification
National Environmental Policy Act
The 1982 amendments to the ESA, in
section 4(b)(1)(A), restrict the
information that may be considered
when assessing species for listing to the
best scientific and commercial data
available. Based on this limitation of
criteria for a listing decision and the
opinion in Pacific Legal Foundation v.
Andrus, 657 F 2d 829 (6th Cir.1981), we
have concluded that ESA listing actions
are not subject to the environmental
assessment requirements of the National
Environmental Policy Act. (see also
NOAA Administrative Order 216 6.)
Executive Order (E.O.) 12866,
Regulatory Flexibility Act
As noted in the Conference Report on
the 1982 amendments to the ESA,
economic impacts cannot be considered
when assessing the status of a species.
Therefore, the economic analysis
requirements of the Regulatory
Flexibility Act are not applicable to the
listing process. In addition, this rule is
exempt from review under E. O. 12866.
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Paperwork Reduction Act
This proposed rule does not contain
a collection-of-information requirement
for the purposes of the Paperwork
Reduction Act.
Federalism
E.O. 13132 requires agencies to take
into account any federalism impacts of
regulations under development. It
includes specific consultation directives
for situations where a regulation will
preempt state law, or impose substantial
direct compliance costs on state and
local governments (unless required by
statute). Neither of these circumstances
is applicable to this proposed listing
determination. In keeping with the
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intent of the Administration and
Congress to provide continuing and
meaningful dialogue on issues of mutual
State and Federal interest, this proposed
rule will be given to the relevant state
agencies in each state in which the
Caribbean monk seal formerly occurred,
and each will be invited to comment.
List of Subjects in 50 CFR Part 224
Administrative practice and
procedure, Endangered and threatened
species, Exports, Imports, Reporting and
recordkeeping requirements,
Transportation.
Dated: June 3, 2008.
Samuel D. Rauch, III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
For the reasons set out in the
preamble, we propose to amend 50 CFR
part 224 as follows:
PART 224—ENDANGERED MARINE
AND ANADROMOUS SPECIES
1. The authority citation for part 224
continues to read as follows:
Authority: 16 U.S.C. 1531 1543 and 16
U.S.C. 1361 et seq.
2. Amend § 224.101(b) by removing
the term ‘‘Caribbean monk seal
(Monachus tropicalis);’’.
[FR Doc. E8–12808 Filed 6–6–08; 8:45 am]
BILLING CODE 3510–22–S
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 600
[Docket No. 070717348–7766–02]
RIN 0648–AV60
Magnuson-Stevens Act Provisions;
Annual Catch Limits; National
Standard Guidelines
National Marine Fisheries
Service (NMFS); National Oceanic and
Atmospheric Administration (NOAA);
Commerce.
ACTION: Proposed rule; request for
comments.
AGENCY:
NMFS proposes revisions to
the guidelines for National Standard 1
(NS1) of the Magnuson-Stevens Fishery
Conservation and Management Act
(MSA). This action is necessary to
provide guidance on how to comply
with new annual catch limit (ACL) and
accountability measure (AM)
requirements for ending overfishing of
fisheries managed by federal fishery
SUMMARY:
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management plans (FMPs). It also
clarifies the relationship between ACLs,
maximum sustainable yield (MSY),
optimum yield (OY), and other
applicable reference points. The intent
of this action is to facilitate compliance
with requirements of the MagnusonStevens Act to end and prevent
overfishing, rebuild overfished stocks
and achieve OY.
DATES: Comments must be received by
September 8, 2008.
ADDRESSES: You may submit comments,
identified by 0648-AV60, by any of the
following methods:
• Electronic Submissions: Submit all
electronic public comments via the
Federal e-Rulemaking portal: https://
www.regulations.gov;
• Fax: 301–713–1193, Attn: Mark
Millikin;
• Mail: Mark R. Millikin, National
Marine Fisheries Service, NOAA, Office
of Sustainable Fisheries, 1315 East-West
Highway, Room 13357, Silver Spring,
MD 20910 (mark outside of envelope
‘‘Comments on Annual Catch Limits
proposed rule’’);
Instructions: All comments received
are a part of the public record and will
generally be posted to https://
www.regulations.gov without change.
All Personal Identifying Information (for
example, name, address, etc.)
voluntarily submitted by the commenter
may be publicly accessible. Do not
submit confidential business
information or otherwise sensitive or
protected information.
NMFS will accept anonymous
comments. Attachments to electronic
comments will be accepted in Microsoft
Word, Excel, Wordperfect, or Adobe
PDF file formats only.
Copies of the Regulatory Impact
Review (RIR)/Regulatory Flexibility Act
Analysis (RFAA) for this proposed rule
are available from Mark R. Millikin at
the address listed above. The RIR/RFAA
document is also available via the
internet at https://www.nmfs.noaa.gov/
msa2007/catchlimits.htm.
FOR FURTHER INFORMATION CONTACT:
Mark R. Millikin, Senior Fishery
Management Specialist, 301–713–2341.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Overview of Proposed Revisions
II. Acronyms
III. Background
IV. NMFS’s Proposed Rule for Further
Revisions to NS1 Guidelines in 2005
V. NMFS’s Initial Action on MSRA
Requirements for ACLs
VI. MSRA Ending Overfishing Requirements
VII. Reasons for Overfishing and
Expectations for ACLs to Prevent/End
Overfishing
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VIII. Definition, Interpretation, and
Application of the Term ‘‘Fishery’’ and
Its Relevance to ACLs
A. Stocks in the Fishery
B. Ecosystem Component Species
C. Stocks Identified in More Than One
FMP
D. Stock Complexes
IX. Statutory Exceptions to Requirements for
ACLs and AMs and Flexibility in
Application of the NS1 Guidelines
X. MSRA Requirements for SSCs Related to
ACLs
XI. MSY, OY, and SDC: A Review
XII. Description of the Relationship of OFL
to MSY and ACT to OY
XIII. Definition Framework for OFL, ABC,
ACL, and ACT
XIV. Control Rules
XV. Sector ACLs, ACTs, and AMs
XVI. Accountability Measures
XVII. Summary of Items to Include in FMPs
XVIII. Change in Timetable When
Establishing a Rebuilding Plan
XIX. Establishing the Length of Time for a
Rebuilding Plan
XX. Action When a Stock’s Rebuilding Plan
Ends and the Stock Is Not Rebuilt
XXI. Changes to the definitions of Some
Components of MSY
XXII. Social, Economic and Ecological
Factors as They Relate to OY
XXIII. Scope of This Proposed Action
XXIV. Republishing Codified Text in Its
Entirety
XXV. Classification
I. Overview of Proposed Revisions
NMFS fulfills the requirements of
section 301(b) of the Magnuson-Stevens
Act—‘‘The Secretary shall establish
advisory guidelines (which shall not
have the force and effect of law), based
on national standards, to assist in the
development of fishery management
plans,’’ with its national standard
guidelines that appear at 50 CFR
600.310 through 50 CFR 600.355. NMFS
is proposing revisions to the NS1
guidelines to address, among other
things, new requirements for fisheries
undergoing overfishing, to have ACLs
and AMs to end overfishing by 2010,
and all fisheries to have ACLs and AMs
in place to prevent or end overfishing by
2011, and beyond. A stock or stock
complex may not require an ACL and
AMs if it qualifies for a statutory
exception under the Magnuson-Stevens
Act. Other proposed revisions to the
NS1 guidelines include: (1) A
description of the relationship between
MSY, OY, overfishing limits (OFL),
acceptable biological catch (ABC),
ACLs, and annual catch targets (ACTs);
(2) guidance on how to combine the use
of ACLs and AMs for a stock to prevent
overfishing when possible, and adjust
ACTs or ACLs, or both, and AMs, if an
ACL is exceeded; (3) allowing for
inclusion of ecosystem component (EC)
species in FMPs and, in such cases,
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guidance for how to classify which
stocks are ‘‘in the fishery’’ and which
species are ecosystem components; (4)
replacing MSY control rules with ABC
control rules and replacing OY control
rules with ACT control rules; (5) new
requirements for scientific and
statistical committees (SSC); (6)
changing the timeline to prepare new
rebuilding plans; (7) revised guidance
on how to establish rebuilding time
targets; and (8) advice on action to take
at the end of a rebuilding period if a
stock is not yet rebuilt.
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II. Acronyms
ABC—acceptable biological catch
ACL—annual catch limit
ACT—annual catch target
AM—accountability measures
ANPR—Advance Notice of Proposed
Rulemaking
Bmsy—MSY stock size
EC—ecosystem component species
EEZ—Exclusive Economic Zone
Fmsy—MSY fishing mortality rate
FMP—fishery management plan
MFMT—maximum fishing mortality
threshold
MSA—Magnuson-Stevens Act
MSRA—Magnuson-Stevens Fishery
Conservation and Management
Reauthorization Act
MSST—minimum stock size threshold
MSY—maximum sustainable yield
NOI—Notice of Intent
NS1—National Standard 1
OFL—overfishing limit
OY—optimum yield
SDC—status determination criteria
SFA—Sustainable Fisheries Act
SSC—scientific and statistical
committee
Tmax—maximum time allowable for
rebuilding a stock
Tmin—minimum time for rebuilding a
stock
Ttarget—target time for rebuilding a stock
(efficiency), and 7 (costs and benefits);
and adding new guidelines for National
Standards 8 (communities), 9 (bycatch),
and 10 (safety of life at sea).
The guidelines for NS1 were revised
extensively in the final rule published
on May 1, 1998, to bring them into
conformance with revisions to the MSA,
as amended in 1996 by the Sustainable
Fisheries Act (SFA). In particular, the
1998 revisions to the NS1 guidelines
addressed new requirements for FMPs
brought about by SFA amendments to
MSA section 304(e) (rebuilding
overfished fisheries).
The Magnuson-Stevens Fishery
Conservation and Management
Reauthorization Act of 2006 (MSRA),
which President Bush signed into law
on January 12, 2007, included new
requirements regarding preventing and
ending overfishing and rebuilding
fisheries. Therefore, NMFS is proposing
revisions to the NS1 guidelines at 50
CFR 600.310, to integrate these new
requirements with existing provisions
related to overfishing, rebuilding
overfished stocks, and achieving
optimum yield.
IV. NMFS’s Proposed Rule for Further
Revisions to NS1 Guidelines in 2005
III. Background
The MSA serves as the chief authority
for fisheries management in the U.S.
Exclusive Economic Zone (EEZ).
Section 301(b) of the MSA requires that
‘‘The Secretary shall establish advisory
guidelines (which shall not have the
force and effect of law), based on the
national standards, to assist in the
development of fishery management
plans.’’ Guidelines for the national
standards are codified in subpart D of 50
CFR part 600. The guidelines for
national standards were last revised
through a final rule published in the
Federal Register on May 1, 1998 (63 FR
24212), by adding revisions to the
guidelines for National Standards 1
(optimum yield), 2 (scientific
information), 4 (allocations), 5
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NMFS published an advance notice of
proposed rulemaking (ANPR) in 2003
(68 FR 7492, February 14, 2003), and a
proposed rule in 2005 (70 FR 36240,
June 22, 2005), in the Federal Register
to propose further revisions to the NS1
guidelines. NMFS sought to improve the
utility of the 1998 guidelines in
assisting the regional fishery
management councils, and the Secretary
of Commerce (Secretary) in the case of
a Secretarial Amendment or a
Secretarial FMP (denoted collectively
hereafter as ‘‘Councils,’’ as 50 CFR
600.305(c)(11) provides that ‘‘Council’’
includes both the regional fishery
management councils and the Secretary
when preparing FMPs or amendments),
when establishing or revising status
determination criteria (SDC) for
overfishing and overfished definitions
for stocks, and constructing or revising
rebuilding plans for overfished stocks.
Although NMFS received many
public comments on the ANPR and the
2005 proposed rule, NMFS decided not
to pursue publication of a final rule
when it learned that Congress was
preparing an amendment to the MSA
that seemed likely to revise how to
manage stocks undergoing overfishing
and stocks that need a rebuilding plan.
Congress’s efforts culminated in passage
of the 2006 MSRA.
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V. NMFS’s Initial Action on MSRA
Requirements for ACLs
NMFS published a notice of intent
(NOI) to prepare an environmental
impact statement (EIS) and
commencement of a scoping period for
ACLs and AMs in the Federal Register
on February 14, 2007 (72 FR 7016), with
a comment period ending date of April
17, 2007. NMFS held nine scoping
sessions, one associated with each of the
eight Regional Fishery Management
Councils’ meetings and one at NMFS
Headquarters in Silver Spring, MD.
Comments that NMFS received are
contained in ‘‘Summary of Comments
Received on NMFS Proposal to Develop
Guidance on ACLs and AMs, July
2007,’’ that is available at the NMFS
Web site: https://www.nmfs.noaa.gov/
msa2007/catchlimits.htm.
The NOI indicated that an
environmental assessment or EIS would
be prepared for this action. However,
NMFS has decided that, for purposes of
compliance with the National
Environmental Policy Act, a categorical
exclusion is appropriate for this action.
The proposed action would provide
general guidance on ACL and AM and
other requirements, but there is
considerable diversity in federallymanaged fisheries and FMPs. Thus, any
analysis of the environmental,
economic, and social impacts of the NS1
guidelines would be highly speculative.
Potential environmental, economic, and
social impacts cannot be meaningfully
analyzed until the Councils apply the
guidelines to specific fisheries and
FMPs. At that time, the Councils would
prepare an EIS or EA, as appropriate.
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VI. MSRA Ending Overfishing
Requirements
Section 104(a)(10) of the MSRA
established new requirements to end
and prevent overfishing, including
ACLs and AMs. Section 303(a)(15) was
added to the MSA to read as follows:
‘‘establish a mechanism for specifying
annual catch limits in the plan
(including a multiyear plan),
implementing regulations, or annual
specifications, at a level such that
overfishing does not occur in the
fishery, including measures to ensure
accountability.’’ ACLs and AMs are
required by fishing year 2010 if
overfishing is occurring in a fishery, and
they are required for all other fisheries
by fishing year 2011.
In practical terms, given the time it
takes to prepare and implement an FMP
amendment, if the status of one or more
stocks in a fishery at the end of 2008 is
‘‘subject to overfishing,’’ Councils
should submit ACL and AM
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mechanisms and actual ACLs for that
fishery to be effective in fishing year
2010. If overfishing is determined to be
occurring in a fishery in 2009, Councils
should submit ACL and AM
mechanisms and actual ACLs for that
fishery to be effective in fishing year
2010, if possible, or in fishing year 2011,
at the latest. All fisheries must have
ACL and AM mechanisms and actual
ACLs by the fishing year 2011, and
beyond. The Secretary should amend
Secretarial FMPs, to comply with ACL
and AM requirements on the same
timetable. Section 305(c) of the MSA,
which was unchanged by MSRA, also
provides authority to the Secretary to
promulgate emergency regulations or
interim measures necessary to address
an emergency or overfishing for any
fishery without regard to whether an
FMP exists for such fishery.
NMFS recognizes that the phrase, ‘‘at
a level such that overfishing does not
occur’’ in section 303(a)(15) of the MSA
is subject to different interpretations, as
reflected in the varying comments
received during scoping. On the one
hand, the phrase could be interpreted to
mean that overfishing is strictly
prohibited at any cost. On the other
hand, section 303(a)(15) refers to a
‘‘mechanism’’ for setting ACLs,
including AMs, which seems to imply a
more dynamic process that allows for
adjustment of management measures as
a fishery is carried out. The only way to
ensure absolutely no overfishing occurs
is to stop fishing. As long as fishing
occurs, there is a chance for occasional
instances of overfishing due to scientific
uncertainty of data, influence of nonfishing factors, and management
uncertainty. Continued overfishing for a
period of years (chronic overfishing),
presents the greatest danger to the
health of fish stocks, and often leads to
stocks becoming overfished. NMFS has
noted that overfished stocks with
chronic overfishing seem to seldom
rebuild, whereas overfished stocks that
are rarely subject to overfishing have a
better chance of rebuilding.
Taking the above considerations into
account, NMFS believes that the ACL
requirement should be interpreted to
provide for some flexibility given
scientific and management uncertainty
and other factors, but at the same time,
must address overfishing and facilitate
rebuilding. Chronic overfishing can be
prevented by ensuring that the
combination of ACLs and AMs decrease
the risk of future overfishing each
successive time an ACL is exceeded.
NMFS thus proposes a performance
standard such that if catch of a stock
exceeds its ACL more often than once in
the last four years (i.e., more often than
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25 percent of the time), then the system
of ACLs, ACTs and AMs should be reevaluated to improve its performance
and effectiveness (see § 600.310(g)(3) in
this proposed action). NMFS believes
that allowing a higher frequency of the
ACL being exceeded would not
safeguard enough against overfishing. A
Council could choose a higher
performance standard (e.g., a stock’s
catch should not exceed its ACL more
often than once every five or six years)
for a stock that is particularly vulnerable
to the effects of overfishing.
VII. Reasons for Overfishing and
Expectations for ACLs to Prevent/End
Overfishing
The ‘‘NMFS Fourth Quarterly Report
for 2007 Status of U.S. Fisheries’’
indicates that 41 stocks managed by
federal FMPs were undergoing
overfishing as of December 31, 2007.
Stocks become listed as ‘‘overfishing’’ or
remain in an overfishing status for a
variety of reasons, including:
1. The goal of the FMP may be to end
overfishing over several years by
gradually reducing fishing mortality
rates instead of ending overfishing
immediately.
2. Management measures have proven
ineffective at ending overfishing (e.g.,
lack of inseason closure authority for
the fishery or management measures are
aimed at achieving a target catch that is
set too close to the catch amount that
results in overfishing, or both).
3. Management measures to address
overfishing have not been implemented
yet.
4. Recent change in scientific advice
(i.e., the Council has not had sufficient
time to amend the FMP and no
automatic measures exist in the FMP to
make necessary adjustments to end
overfishing in the subsequent fishing
year).
5. Bycatch mortality in other fisheries
has not been addressed adequately or is
poorly known.
6. Data sufficient to verify whether or
not overfishing is occurring are not
available, so the existing overfishing
determination is retained.
7. International fishing pressure is
responsible for the large majority of
overfishing.
8. Fishing pressure in state or
territorial waters is responsible for the
large majority of overfishing, federal
action alone is not sufficient to end
overfishing, and managers in the various
jurisdictions are unable thus far to agree
on a concerted approach for preventing
overfishing.
NMFS believes that the ACL and AM
requirements will address overfishing
that results from reasons 1, 2, 3, and 4
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above. Better scientific data, along with
adequate ACLs and AMs, should enable
Councils to prevent overfishing for
reasons 5 and 6. Stocks that are
undergoing overfishing for reason 7
would be exempt from the ACL
requirement (see §§ 600.310(h)(2)(ii) and
600.310(k) of this proposed action for
discussion of international fisheries).
There may be circumstances where
managers in various jurisdictions are
unable to agree on an ACL and AMs that
would end or prevent overfishing for a
fishery described under reason 8. In
such cases, these proposed guidelines
would require an ACL for the overall
fishery, but AMs would be implemented
only for the portion of the fishery under
federal management authority.
VIII. Definition, Interpretation, and
Application of the Term ‘‘Fishery’’ and
Its Relevance to ACLs
The MSA, as amended by MSRA,
requires that a Council shall develop
ACLs ‘‘for each of its managed fisheries’’
(see MSA section 302(h)(6)) and as
noted earlier, that each FMP have a
mechanism for specifying ACLs ‘‘at a
level such that overfishing does not
occur in the fishery’’ (see MSA section
303(a)(15)). Consistent with these
sections of the MSA, the proposed NS1
guidelines provide that ACLs and AMs
are needed for each ‘‘fishery’’ under
federal FMP management, unless
covered by a statutory exception.
The MSA defines ‘‘fishery’’ broadly,
and this definition did not change with
the passage of the MSRA. A ‘‘fishery’’ is
‘‘one or more stocks of fish which can
be treated as a unit for purposes of
conservation and management and
which are identified on the basis of
geographical, scientific, technical,
recreational and economic
characteristics,’’ and ‘‘any fishing of
such stocks’’ (see MSA section 3(13) and
50 CFR 600.10). The term ‘‘fishery’’ can
mean different things in different
contexts. For example, when dealing
with biological concepts such as
determining a status of overfishing or
overfished, the NS1 guidelines generally
apply at the ‘‘stock or stock complex’’
level (See, e.g., 50 CFR 600.310(c)(1), (d)
(defining MSY and ‘‘overfish’’ with
regard to ‘‘stock or stock complex’’) and
§ 600.305(c)(12) (explaining that ‘‘stock
or stock complex’’ is used as a synonym
for ‘‘fishery’’ in NS guidelines). In other
instances, such as managing a fishery
for OY, the term ‘‘fishery’’ is viewed
more broadly (see 50 CFR 600.310(f)
(referring to OY at the ‘‘fishery’’ and not
the ‘‘stock or stock complex’’ level)).
Given the broad definition of
‘‘fishery,’’ the Councils have had, and
continue to have, considerable
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discretion in defining the ‘‘fishery’’
under FMPs. Some FMPs include only
one or a few stocks whereas others
include several or hundreds of species.
Looking at existing FMPs, the primary
reasons why stocks are included in
FMPs are because people seek to harvest
them for sale or personal use (i.e., the
fish are the target of fishing activity), or
they are caught incidentally in the
pursuit of harvesting one or more other
stocks and could experience overfishing
or become overfished without
conservation and management
measures. These reasons are consistent
with the stated purposes of the MSA,
which includes the preparation and
implementation of FMPs ‘‘which will
achieve and maintain, on a continuing
basis, the optimum yield from each
fishery’’ (see MSA section 2(b)(4)). OY
is defined with regard to ‘‘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’’
(see MSA section 3(33)).
While the focus of FMPs has been
stocks managed for OY, in recent years,
some FMPs have included other stocks
in an effort to incorporate ecosystem
approaches to management. Congress
acknowledged this increased attention
to ecosystem approaches in the
‘‘Findings’’ section of the Act (see MSA
section 2(a)(11) (acknowledging that a
number of Councils have demonstrated
significant progress in integrating
ecosystem considerations under existing
authorities of the MSA)). In addition,
MSRA added a new section 303(b)(12)
that provides that an FMP may ‘‘include
management measures in the plan to
conserve target and non-target species
and habitats, considering the variety of
ecological factors affecting fishery
populations.’’
NMFS wants to encourage ecosystem
approaches to fishery management and
believes that clarification of what
constitutes the ‘‘fishery’’ would be
helpful. As such, NMFS is proposing
guidance pertaining to ‘‘stocks in the
fishery’’ and ‘‘ecosystem component
(EC) species,’’ which are described in
detail below. The intent of this guidance
is to articulate approaches taken under
existing FMPs and to provide a
framework for thinking about future
FMPs and FMP amendments. The
Councils would have the discretion to
determine, on a case-by-case basis,
whether changes in their stock
classifications under current FMPs are
needed.
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A. Stocks in the Fishery
As a default, all stocks currently
identified in an FMP are considered
‘‘stocks in the fishery.’’ ‘‘Stocks in the
fishery’’ would include target stocks
(i.e., stocks that fishers seek to catch for
sale or personal use, including
‘‘economic discards’’ as defined under
MSA section 3(9)), non-target stocks that
are retained for sale or personal use, and
non-target stocks that are not retained
for sale or personal use and that are
either determined to be subject to
overfishing, approaching overfished, or
overfished, or could become so,
according to the best scientific
information available, without
conservation and management measures
(see Figure 1 and § 600.310(d)(2) of this
proposed action). Stocks and stock
complexes in the fishery should have
quantitative SDC, MSY, ABC, ACL, and
ACT (collectively called ‘‘reference
points’’ throughout this section) and
AMs (see Table 1 for reference points
needed for different types of stocks, and
see § 600.310(b)(2)(iv) of this proposed
action), although some stocks in the
fishery may not require ACLs and AMs
if they are covered by a statutory
exception (see § 600.310(h)(2) of this
proposed action). Hereafter, in these
guidelines, ‘‘stock’’ or ‘‘stock(s) and
stock complex(es)’’ refer to ‘‘stocks in
the fishery.’’
B. Ecosystem Component Species
Beyond the ‘‘stocks in the fishery,’’ a
Council may, but is not required to,
include EC species in an FMP. Such
species would include non-target fish
species that are not considered part of
the ‘‘fishery’’ but rather species with
which the fishery may occasionally
interact (i.e., catch) (see § 600.310(d)(5)
of this proposed action). A Council may
choose to include EC species for
purposes of incorporating ecosystem
approaches to fishery management, data
collection, etc. Identification of EC
species must be done through an FMP
amendment process (see § 600.310(d) of
this proposed action). Such species are
appropriate to consider when
addressing specification of OY and
conservation and management measures
for the fishery (see MSA sections 3(33)
(referring to taking into account the
marine ecosystems in OY definition),
and 3(5) (referring to avoiding
irreversible or long-term effects on
fishery resources and the marine
environment and ensuring multiplicity
of options)). Because EC species are not
considered to be ‘‘in the fishery,’’
specification of reference points, ACLs,
and AMs are not required (see Table 1).
However, a Council should consider
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measures for the fishery to minimize
bycatch and bycatch mortality of EC
species consistent with National
Standard 9, and to protect their
associated role in the ecosystem. NMFS
is especially interested in the public’s
comments on the appropriate criteria for
classification of EC species.
C. Stocks Identified in More Than One
FMP
If a stock is identified as part of more
than one ‘‘fishery,’’ Councils should
choose which FMP will be the ‘‘primary
FMP’’ in which management objectives,
SDC, and other reference points for the
stock are established. In most cases, the
primary FMP for a stock will be the one
in which the stock is identified as a
target stock. Other FMPs in which the
stock is identified as part of a fishery
should contain management measures
consistent with the primary FMP for the
stock.
TABLE 1.—REFERENCE POINTS, ACCOUNTABILITY MEASURES, AND CONTROL RULES THAT WOULD BE REQUIRED OR
RECOMMENDED
Reference points,
accountability measures, and
control rules
MSY 1 .......................................
SDC 1 (e.g. MFMT 2, MSST 2)
OY 1 .........................................
OFL 2 ........................................
ABC 1 .......................................
ACL 1 ........................................
AMs 1 .......................................
ACT 2 .......................................
ABC control rule 2 ....................
ACT control rule 2 ....................
Stocks and stock complexes
in a fishery (excluding those
with an approximate 1 year
life cycle and those managed
under international fishery
agreements)
Stocks and stock complexes
in a fishery that have a life
cycle of approximately 1 year
Stocks and stock complexes
in a fishery managed under an
international fishery
agreement 3
Ecosystem
component
species 4
.............................................
.............................................
At the stock, stock complex,
or fishery level.
R .............................................
.............................................
.............................................
.............................................
.............................................
.............................................
.............................................
.............................................
.............................................
At the stock, stock complex,
or fishery level.
R .............................................
.............................................
Only if ‘‘subject to overfishing’’
Only if ‘‘subject to overfishing’’
Only if ‘‘subject to overfishing’’
.............................................
R .............................................
.............................................
.............................................
R .............................................
N/A
N/A
N/A
R
R
R
R
R
R
R
N/A
N/A
N/A
N/A
N/A
N/A
N/A
.............................................
.............................................
.............................................
.............................................
.............................................
.............................................
.............................................
1 MSA
requirement.
consistency with the NS1 Guidelines.
3 If the stock is in a U.S. FMP and managed under an international fishery agreement to which the U.S. is party.
4 Not required by MSA, but an option provided in the NS1 Guidelines.
Legend:
= Yes, this is applicable.
ABC = Acceptable Biological Catch.
ACL = Annual Catch Limit.
AM = Accountability Measures.
MFMT = Maximum Fishing Mortality Threshold.
MSST = Minimum Stock Size Threshold.
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MSY = Maximum Sustainable Yield.
N/A = Not Applicable.
OFL = Overfishing Limit.
OY = Optimum Yield.
R = Recommended.
SDC = Status Determination Criteria.
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D. Stock Complexes
‘‘Stock complex’’ means a group of
stocks in an FMP that are sufficiently
similar in geographic distribution, life
history, and vulnerability to the fishery
that the impacts of management actions
on the stocks in the complex is similar
(see § 600.310(d)(8) of this proposed
action). Stock complexes may be
comprised of: (1) One or more indicator
stocks, each of which has SDC and
ACLs, and several other stocks; (2)
several stocks without an indicator
stock, with SDC and an ACL for the
complex as a whole; or (3) one or more
indicator stocks, each of which has SDC
and management objectives, with an
ACL for the complex as a whole (this
situation might be applicable to some
salmon species).
For stock complexes, the SDC
measured on a stock complex-wide
basis or for an indicator stock should
satisfy the MSA’s requirements to
prevent overfishing and achieve OY for
a fishery. Vulnerability of stocks to the
fishery should be evaluated when
determining if: (1) A particular stock
complex should be established or
reorganized; (2) a particular stock
should be a member of a stock complex;
or (3) a stock complex should be
reorganized. Indicator stocks are stocks
selected as a representative for a stock
complex because they have known
determinations regarding SDC, and
known values for MSY and OY, and can
form the basis for an MSY and OY for
the combinations of stocks in a
complex. Although it is common for the
indicator stock for a stock complex to be
the most abundant stock, if an indicator
stock is less vulnerable than other
stocks in the complex, the management
measures should be more conservative
to protect the more vulnerable stocks
from overfishing.
IX. Statutory Exceptions to
Requirements for ACLs and AMs and
Flexibility in Application of NS1
Guidelines
The MSRA provides two statutory
exceptions to the ACL and AM
requirements under MSA section
303(a)(15) (see MSRA section 104(b)
(adding two exceptions under a MSA
section 303 note); see also
§ 600.310(h)(2) of this proposed action).
First, MSA section 303(a)(15) ‘‘shall not
apply to a fishery for species that have
a life cycle of approximately 1 year
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unless the Secretary has determined the
fishery is subject to overfishing of that
species’’ (see MSRA section 104(b)(2)).
NMFS interprets ‘‘fishery for species’’ to
be a stock. In addition, NMFS interprets
‘‘a life cycle of approximately 1 year’’ to
mean that the average length of time it
takes for an individual to produce a
reproductively active offspring is
approximately 1 year, and that the
individual has only one breeding season
in its lifetime. While stocks that qualify
for the 1-year life cycle exception would
not need to have ACLs and AMs, such
stocks should still have SDC, MSY, OY,
ABC, and an ABC control rule.
Second, MSA section 303(a)(15) shall
take effect in 2010 and 2011, as
discussed earlier, ‘‘unless otherwise
provided for under an international
agreement in which the United States
participates’’ (see MSRA section
104(b)(1)). It is not clear to what the text
‘‘unless otherwise provided for’’ is
referring. NMFS has considered several
possible interpretations of this text in
light of other provisions in MSRA,
including the new international
overfishing provisions in MSA section
304(i). Prior to MSRA, fisheries
managed under international
agreements in which the United States
participates (referred to in this action as
‘‘international fisheries’’) were subject
to MSA section 304(e) requirements
regarding overfishing and rebuilding.
However, in many of these fisheries, the
United States could not unilaterally end
overfishing or rebuild the stocks. New
MSA section 304(i) and other MSRA
provisions acknowledge the increasing
problem of international overfishing and
the challenges of establishing
conservation and management measures
at the international level. Given
Congress’s recognition of the increasing
problem of international overfishing and
the complexities of international
negotiation, NMFS believes that the
ACL exception should apply to fisheries
that are subject to management under
international agreements in which the
United States participates. Applying
ACLs or AMs only to the U.S. portion
of the catch would not effect rebuilding
or end overfishing, would potentially
disadvantage U.S. fishermen with
respect to foreign fishermen, and could
weaken U.S. negotiating positions at
international fora in which it
participates.
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Apart from the statutory exceptions,
NMFS recognizes that there are limited
circumstances that do not fit the
standard approaches to specification of
reference points and management
measures set forth in the proposed
revisions to the NS1 guidelines. These
include, among other things,
conservation and management of ESAlisted species, harvests from aquaculture
operations, and stocks with unusual life
history characteristics (e.g., Pacific
salmon, where the spawning potential
for a stock is spread over a multi-year
period). For fisheries where ESA-listed
species are incidentally caught, the ESA
recovery plan would be a significant
driver for setting management
objectives, including ACLs, for the
fishery. For aquaculture, once managers
address status of broodstock taken from
the wild (i.e., whether overfishing is
occurring and/or whether the stock is in
need of rebuilding), then the levels of
harvests from an aquaculture facility
would not necessarily need to focus on
ending or preventing overfishing or
rebuilding stocks. In these
circumstances, Councils may propose
alternative approaches for satisfying the
NS1 requirements of the MagnusonStevens Act other than those set forth in
these guidelines. Councils should
document their rationale for any
alternative approaches for these limited
circumstances in an FMP or FMP
amendment, which will be reviewed for
consistency with the Magnuson-Stevens
Act.
For a fishery in a federal FMP that has
a large majority of harvest in state or
territorial waters, the fishery should
have ACL that takes into account the
overall status of the stock, whether in
state or federal waters or beyond.
However, NMFS recognizes that AMs
could only be applied to the portion of
the fishery under federal jurisdiction.
Given the jurisdictional issue, one
approach proposed is that the overall
ACL could be divided into a federal
portion (federal-ACL) and a state
portion (state-ACL). AMs would then be
triggered when the federal-ACL was
reached or projected to be reached (see
further explanation in ‘‘Accountability
Measures’’ section below).
X. MSRA Requirements for SSCs
Related to ACLs
The MSRA added new requirements
for SSCs in the MSA. New section
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302(g)(1)(B) of the MSA states that an
SSC for each Regional Fishery
Management Council ‘‘shall provide its
Council ongoing scientific advice for
fishery management decisions,
including recommendations for
acceptable biological catch, preventing
overfishing, maximum sustainable
yield, and achieving rebuilding targets,
and reports on stock status and health,
bycatch, habitat status, social and
economic impacts of management
measures, and sustainability of fishing
practices.’’ New section 302(g)(1)(E)
provides that ‘‘The Secretary and each
Council may establish a peer review
process for that Council for scientific
information used to advise the Council
about the conservation and management
of the fishery.’’ In addition, new section
302(h)(6) provides that each Regional
Fishery Management Council is
required to ‘‘develop annual catch limits
for each of its managed fisheries that
may not exceed the fishing level
recommendations of its scientific and
statistical committee or the peer review
process established under subsection
(g).’’
NMFS recognizes that there is
variability in the peer review processes
and involvement of SSCs amongst the
various Councils. In addition, the above
statutory sections could be subject to
different interpretations. While MSA
section 302(h)(6) refers generally to
‘‘fishing level recommendations,’’
section 302(g)(1)(B) refers to
recommendations for ABC and MSY,
among other things, and section
302(g)(1)(E) refers generally to
‘‘scientific information.’’ Further, the
text provides for advice from the SSC
but also refers to peer review processes,
leaving open a question about the role
and relationship between the two.
NMFS believes that clear processes for
implementing these provisions are
important in order to ensure that
Councils get the information needed to
establish ACL mechanisms, prevent
confusion in the decision making
process, and ensure general consistency
in approaches taken.
For purposes of setting ACLs, a
critical piece of scientific advice that
Councils will need will be the ABC.
Taking this into account, and
considering the new requirements in
light of existing SSC, Council, and peer
review processes, NMFS proposes that
the Councils establish a process that
could be included in their Statement of
Organization, Practices and Procedures
(see § 600.115) which will: Establish an
ABC control rule, identify the body that
will apply the ABC control rule (i.e.,
calculates the ABC), identify the review
process that will verify the resulting
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ABC, and confirm that the SSC
recommends the ABC to the Council.
For Secretarial FMPs or FMP
amendments, agency scientists or a peer
review process would provide the
scientific advice to establish ABC. For
fisheries managed under international
agreements in which the United States
participates (referred to in this action as
‘‘international fisheries’’), stock
assessments are conducted through
international scientific bodies that may
include U.S. and non-U.S. scientists.
While the United States promotes
fishery conservation and management
principles as embodied in the MSA (see,
e.g., MSA section 102(c)), it cannot
guarantee that international actions will
be consistent with the Act or NS1
guidelines. Thus, an ABC as defined in
these guidelines would not be required
for international fisheries.
For stock and stock complexes
required to have an ABC, NMFS
recommends that each Council should
establish an ABC control rule (see
§ 600.310(f)(4) of this proposed action)
based on scientific advice from its SSC.
The process of establishing an ABC
control rule could also involve science
advisors or the peer review process
established under MSA section
302(g)(1)(E). Stock assessment scientists,
a plan development team, or other
designated body would then apply the
ABC control rule. If a peer review
process is established it should
investigate the technical merits of stock
assessments and other scientific
information used by the SSC. For
example, a peer review process (e.g.,
Stock Assessment Review Panel) could
validate the ABC calculation and then
pass their results to the SSC. Ultimately,
the SSC should make the formal ABC
recommendation to the Council. For
Council-managed fisheries, the peer
review process is not a substitute for the
SSC, and should work in conjunction
with the SSC.
XI. MSY, OY, and SDC: A Review
MSY, OY, and SDC are concepts
described in the current NS1 guidelines,
and MSRA did not effect changes to the
MSA that would require changes to
these concepts. The following sections
provide a review of MSY, OY, and SDC
and an explanation of the relationship
between them and the proposed
guidance on ACLs and other
requirements.
MSY is the largest long-term average
catch or yield that can be taken from a
stock or stock complex under prevailing
ecological and environmental
conditions and fishery technological
characteristics. Any estimate of MSY
depends on the population dynamics of
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the stock and the characteristics of the
fisheries (e.g. gear selectivity). MSY
stock size (Bmsy) is the long-term average
size of the stock or stock complex,
measured in terms of spawning biomass,
or other appropriate measure of the
stock’s reproductive potential, that
would be achieved by fishing at Fmsy.
OY is the amount of fish that will
provide the greatest overall benefit to
the Nation, while preventing
overfishing, particularly with respect to
food production and recreational
opportunities, and taking into account
the protection of marine ecosystems. OY
is prescribed on the basis of the MSY
from the fishery, as reduced by relevant
economic, social or ecological factors. In
the case of an overfished fishery, OY
provides for rebuilding to a level
consistent with producing MSY in such
a fishery. In NS1, use of the phrase,
‘‘achieving, on a continuing basis, the
optimum yield from each fishery’’
means producing, from each stock, stock
complex or fishery a long-term series of
catches such that the average catch is
equal to OY, overfishing is prevented,
the long term average biomass is near or
above Bmsy, and overfished stocks are
rebuilt in as short a time as possible as
specified in MSA section 304(e)(4). OY
might be established at the stock or
stock complex level, or for a fishery
comprised of stocks, many of which
have their own ACL and ACT (e.g.,
groundfish of the Gulf of Alaska and
groundfish of the Bering Sea and
Aleutian Islands).
Section 3(34) of the MSA states that
‘‘overfishing’’ and ‘‘overfished’’ mean a
rate or level of fishing mortality that
jeopardizes the capacity of a fishery to
produce the maximum sustainable yield
on a continuing basis. To reduce
confusion and conform to usage of those
terms in other fisheries worldwide, in
the current NS1 guidelines, NMFS
interpreted these terms so that
‘‘overfished’’ pertains to the biomass of
the stock or stock complex, and
‘‘overfishing’’ pertains to a rate or level
of removal of fish from the stock or
stock complex. The current NS1
guidelines also provide for SDC, which
are quantifiable factors for determining
whether a stock or stock complex is
overfished or if overfishing is occurring.
An overfished definition consists of a
measure of stock abundance called the
minimum stock size threshold (MSST),
below which a stock’s or stock
complex’s capacity to produce MSY on
a continuing basis is jeopardized.
Overfishing of a stock or stock complex
occurs whenever a stock or stock
complex is subjected to a rate or level
of fishing mortality, called the
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maximum fishing mortality threshold
(MFMT), above which the stock’s or
stock complex’s capacity to produce
MSY on a continuing basis is
jeopardized or annual catch exceeds a
stock’s or stock complex’s OFL. MSRA
made no changes to the MSA that would
necessitate different interpretations of
these terms or different approaches to
these concepts.
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XII. Description of the Relationship of
OFL to MSY and ACT to OY
National Standard 1 establishes the
relationship between conservation and
management measures, preventing
overfishing, and achieving OY from
each stock, stock complex or fishery.
The following sections describe in detail
NMFS’ proposed guidance on ACLs and
other new requirements. Among other
things, the proposed guidance
introduces new terms—overfishing limit
(OFL) and annual catch target (ACT)—
which are not set forth in the MSA but
which NMFS believes would be helpful
to implement the statutory
requirements. As an overview, OFL is
an annual amount of catch that
corresponds to the estimate of MFMT
applied to a stock or complex’s
abundance; MSY is the long-term
average of such catches. The current
NS1 guidelines define overfishing with
regard to MFMT, which is a rate of
fishing. The use of OFL would provide
another method for measuring
overfishing by allowing the comparison
of a stock or stock complexes’ annual
catch to its OFL; if catch exceeds OFL,
overfishing is occurring. It is
recommended that ABC would be set
below OFL to take into account the
scientific uncertainty in the estimate of
OFL.
ACL would be the limit that triggers
AMs, and ACT would be the
management target for the fishery.
Management measures for a fishery
should, on an annual basis, achieve the
ACT and prevent the ACL from being
exceeded. The long-term objective is to
achieve OY through annual
achievement of ACT.
XIII. Definition Framework for OFL,
ABC, ACL, and ACT
The MSRA does not define ACLs,
AMs, and ABC, and there are many
different ways in which these terms can
be defined. The voluminous comments
that NMFS received during scoping
reflects the wide range of possible
interpretations and approaches. For
example, some commenters felt that
ACL should be considered a target catch
level and others felt it should be a limit
that should not be approached or
reached. Many commenters suggested,
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in general, that a buffer be implemented
between management targets and limits
in order to prevent overfishing and
account for uncertainty. Over the past
year, NMFS spent considerable time
reviewing different interpretations of
the ACL requirement in light of MSA
sections 303(a)(15), 302(h)(6), and
302(g) and other sections of the MSA,
and taking into consideration the
current NS1 guidelines, previously
proposed changes to those guidelines,
existing FMPs and FMP amendments,
scientific and management roles in the
decision making process, and public
comment. Based on this review, NMFS
proposes the following definitions for
ACL, AM, and ABC, and also for ACT
and OFL:
1. Overfishing limit (OFL) means ‘‘the
annual amount of catch that
corresponds to the estimate of MFMT
applied to a stock or stock complex’s
abundance and is expressed in terms of
numbers or weight of fish.’’ See
§ 600.310(e)(2)(i)(D) of this proposed
action.
2. Acceptable biological catch (ABC)
means ‘‘a level of a stock or stock
complex’s annual catch that accounts
for the scientific uncertainty in the
estimate of OFL and should be specified
based on the ABC control rule.’’ See
§ 600.310 (f)(2)(ii) of this proposed
action.
3. Annual catch limit (ACL) means
‘‘the level of annual catch of a stock or
stock complex that serves as the basis
for invoking accountability measures.’’
See § 600.310(f)(2)(iv) of this proposed
action.
4. Annual catch target (ACT) means
‘‘an amount of annual catch of a stock
or stock complex that is the
management target of the fishery. A
stock or stock complex’s ACT should
usually be less than its ACL and results
from the application of the ACT control
rule. If sector-ACLs have been
established, each one should have a
corresponding sector-ACT.’’ See
§§ 600.310(f)(2)(v) and (f)(6) of this
proposed action.
5. Accountability measures (AMs)
means ‘‘management controls that
prevent ACLs or sector-ACLs from being
exceeded (inseason AMs), where
possible, and correct or mitigate
overages if they occur.’’ See § 600.310(g)
of this proposed action.
As proposed in this action, the
relationship between the above terms
would be OFL≥ABC≥ACL≥ACT (see
Figure 2). Because a primary goal of the
MSA, and management responsibility of
NMFS and the Councils, is to end and
prevent overfishing, rather than account
for it after it occurs, NMFS believes that
a good approach to management is to
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have OFL>ABC and ACL>ACT. The
ABC is lower than the OFL to address
scientific uncertainty in the estimate of
OFL, and ACT is lower than the ACL to
address uncertainty in the accounting
for catch and in the degree to which
management measures can control catch
to the target level.
OFL is an annual amount of catch that
corresponds to the estimate of MFMT
applied to a stock or complex’s
abundance, and MSY is the long-term
average of such catches. NMFS proposes
that OFL be the upper bound of ABC,
but that ABC should usually be reduced
from the OFL to account for scientific
uncertainty in the estimate of OFL. For
overfished stocks, ABC must also be set
to reflect the annual catch that is
consistent with the rebuilding plan for
that stock. Therefore, if a stock is being
managed under a rebuilding program,
its ABC should be lower during some or
all stages of rebuilding than when the
stock is rebuilt. The ABC will be set on
the basis of the ABC control rule.
The proposed guidelines would have
the Councils set the ACL as a level of
catch specified for a stock or stock
complex each year that cannot exceed
its ABC. If a stock or stock complex’s
catch exceeds its ACL, AMs will be
invoked as specified in the FMP. The
ACL may typically be equal to the ABC
and setting the ACL provides an
opportunity to divide the total ACL into
sector-specific ACLs. As noted above,
the purpose of the ACT is to address
management uncertainty. The ACT
would be the target catch of a stock or
stock complex that a fishery is managed
to attain and should generally be less
than the stock or stock complex’s ACL.
‘‘Catch’’ includes fish that are retained
for any purpose, as well as mortality of
fish that are discarded (see
§ 600.310(f)(2)(i) of this proposed
action). Therefore, for fisheries where
bycatch estimates are not available in a
timely enough manner to manage
annual catch, targets may be specified
for landings, so long as an estimate of
bycatch is accounted for such that total
of landings and bycatch will not exceed
the stock’s or stock complex’s ACL. For
a stock with sufficient inseason data
monitoring, the fishery for that stock
would be closed in time to prevent the
ACL from being exceeded.
NMFS notes that when it published
an initial notice about ACLs, ACT was
not a parameter used when exploring
the concept of how to make ACLs and
AMs operational. At that time, NMFS
suggested an initial approach of
OFL>ABC≥ACL with ACL as the target
catch that management measures should
try to attain. Under that approach, if
catch of a stock reached the OFL, its
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‘‘limit.’’ Also, the framework contained
in this proposed rule provides for better
separation between scientific
uncertainty in estimating OFL (i.e., a
recommendation that ABC be lower
than OFL), and management uncertainty
and OY factors indicating that an ACT
be lower than the ACL.
XIV. Control Rules
Control rules are harvest strategies
that specify how a stock’s or stock
complex’s catch will be modified in
response to one or more factors,
particularly estimated stock size. The
current NS1 guidelines include MSY
control rules which are ‘‘limit’’ control
rules and OY control rules which are
‘‘target’’ control rules. For any stock, the
limit control rule results in a higher
amount than the target control rule for
a given stock abundance. Because of the
new MSA requirement for annual catch
limits to end and prevent overfishing for
stocks in a fishery, NMFS proposes that
MSY control rules be replaced by ABC
control rules and become the new limit
control rule, and OY control rules be
replaced by ACT control rules and
become the new target control rule. This
would align the control rules more
directly with the new requirement to
specify an ABC and an ACL for stocks
in the fishery (see earlier discussion in
the preamble for the relationship
between OFL and MSY, and between
ACT and OY).
ABC and ACT control rules should be
developed for each stock when possible.
For stock complexes, ABC and ACT
control rules should be developed for
each indicator stock or for the stock
complex as a whole. ACTs should be set
with the intention that they typically
will be achieved. A stock’s or stock
complex’s ACT control rule should
result in lower target catches than the
ABC control rule would, for all levels of
a stock’s or stock complex’s abundance.
In the proposed revisions to NS1
guidelines, an ABC control rule is a
specified approach to setting the ABC
for a stock or stock complex as a
function of the scientific uncertainty in
the estimate of OFL. An ACT control
rule is an approach to setting the ACT
for each stock and stock complex such
that the risk of exceeding ACL due to
management uncertainty (ability to
control catch and variability in catch
data) is an acceptably low level. Both
control rules are designed to reduce the
risk that overfishing will occur.
For rebuilding stocks, the ABC, ACL,
and ACT should be set at lower levels
than for rebuilt stocks because two
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fishery would be closed. During the
scoping period, NMFS received some
public comments expressing concern
about the use of an ACL as a
management target as opposed to a
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objectives are combined. First,
overfishing should not occur; and
second, rebuilding at a rate
commensurate with the stock’s
rebuilding plan should occur. This
means that, for a rebuilding stock, a
lower target fishing mortality rate may
be needed to accomplish rebuilding, in
addition to avoiding overfishing (i.e.,
ACL and ACT are lower than they
would be if the stock was rebuilt).
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XV. Sector ACLs, ACTs, and AMs
A Council may decide, but is not
required, to divide the ACL into sectorACLs. ‘‘Sector’’ for purposes of the NS1
guidelines means a distinct user group
to which separate management
strategies and catch quotas apply.
Examples of sectors could include the
commercial sector, recreational sector,
or various gear groups within a fishery.
It is up to each Council to decide how
to designate sectors, if any. If sectorACLs are established, sector-AMs and
sector-ACTs must be developed for each
sector-ACL. In cases where states
cooperatively manage a stock, it is
possible that a sector ACL could be
further subdivided in order to establish
‘‘subsector’’ ACLs and ACTs for various
states to align with current management
of catch limits or quotas in the state
fisheries. The system of ACLs and AMs
must be effective and equitable and
protect the stock as a whole from
overfishing. The sum of a stock’s sectorACLs must not exceed the stock’s ACL.
If sector-ACLs and sector-AMs are
established, additional AMs at the stock
level would also be appropriate. A
sector must be closed inseason if timely
catch data indicates its ACL has been
reached. If a sector does not have timely
inseason fisheries data, or has a history
of annual overages, then a Council
should establish a large enough
difference between a sector’s ACT and
ACL to improve the probability that the
sector-ACL and the stock’s ACL are not
exceeded.
XVI. Accountability Measures
AMs are management controls
implemented for stocks such that
exceeding the ACL or sector-ACL is
prevented, where possible, and
corrected or mitigated if it occurs (see
§ 600.310(g) of this proposed action).
AMs include: (1) Those that are applied
inseason and designed to prevent the
ACL from being reached; (2) measures
applied after the fishing year that are
designed to address the operational
issue that caused the ACL overage,
ensuring it does not happen in
subsequent fishing years, and, as
necessary, address any biological harm
to the stock; and (3) those based on
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multi-year average data which are still
reviewed and applied annually (see
discussion below). AMs should address
and minimize both the frequency of
overages and the magnitude of an
overage. AMs should be designed so
that if an ACL is exceeded, specific
adjustments are effective in the next
fishing year, or as soon as possible, with
explanation of why more timely
adjustment is not possible.
If timely inseason fishery catch data
are available for a stock, Councils
should ensure their FMPs contain
inseason closure authority as an AM to
prevent a stock’s ACL from being
exceeded. Where fishery catch data are
not timely enough to implement
inseason AMs, the ACT should be
adjusted downward from the ACL to
account for the increased management
uncertainty and the delayed ability to
implement AMs.
A ‘‘multiyear plan’’ as referenced in
section 303(a)(15) of the MSA is a plan
that establishes harvest specifications or
harvest guidelines for each year of a
time period greater than one year.
Because ‘‘multiyear plans’’ establish
ACLs and ACTs for more than one year
at a time, they should include AMs that
provide if an ACL is exceeded in one
year, then a subsequent year’s harvest
specification (including ACLs and
ACTs) could be revised (see
§ 600.310(f)(5)(i) of this proposed
action).
Some fisheries have highly variable
annual catches and lack reliable
inseason or annual data on which to
base AMs. If there are insufficient data
upon which to compare catch to ACL,
either inseason or on an annual basis, a
Council could base AMs on comparison
of average catch to average ACL over a
three-year moving average period or, if
supported by analysis, some other
appropriate multi-year period (see
§ 600.310(g)(4) of this proposed action).
As a performance standard, if the
average catch exceeds the average ACL
more than once in the last four years,
then the ACL, ACT and AM system
should be re-evaluated to improve its
performance. The initial ACL and
management measures should
incorporate information from previous
years so that AMs based on average
ACLs can be applied from the first year.
If a stock is in a rebuilding plan and
its ACL is exceeded, the AMs should
include overage adjustments that reduce
the ACL in the next fishing year by the
full amount of the overage, unless the
best scientific information available
shows that a reduced overage
adjustment is sufficent, or no
adjustment is needed to mitigate the
effects of the overage. This AM is
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important to increase the likelihood that
the stock will continue to rebuild.
As discussed earlier, stocks and stock
complexes in federal FMPs that have a
large majority of harvest in state or
territorial waters should have an ACL
that takes into consideration the overall
status of the stock. However, federal
management would be limited to that
portion of the fishery under federal
jurisdiction. Options for AMs that a
Council could consider for stocks or
stock complexes caught mostly in state
or territorial waters would include, but
are not limited to: (1) Close the EEZ
when the federal portion of the ACL is
reached, or (2) close the EEZ when the
overall stock or stock complex’s ACL is
reached. The AMs should ensure that
federal managers are doing as much as
possible to end and prevent overfishing.
When stocks are co-managed by federal,
state, tribal, and/or territorial fishery
managers, the goal should be to develop
collaborative conservation and
management strategies, and scientific
capacity to support such strategies, to
prevent overfishing of shared stocks and
ensure their sustainability.
XVII. Summary of Items To Include in
FMPs
This section provides a summary of
items that Councils should include in
their FMPs and FMP amendments in
order to address ACL, AM, and other
aspects of the proposed NS1 guidelines.
Some items are specific to new MSRA
provisions. Others were required prior
to MSRA, but are included here so as to
be comprehensive. Councils may review
their FMPs to decide if all stocks are ‘‘in
the fishery’’ or whether some fit the
category of ‘‘ecosystem component
species’’ and amend their FMP as
appropriate. If they do not establish EC
species through an FMP amendment,
then all stocks in an FMP are presumed
to be ‘‘in the fishery.’’ For all stocks and
stock complexes that are in the fishery,
the Councils should evaluate and
describe the following items in their
FMPs and amend the FMPs, if
necessary, to align their management
objectives to end or prevent overfishing
(see § 600.310(c) of this proposed
action): (1) MSY and SDC, (2) OY at the
stock, stock complex or fishery level, (3)
ABC control rule, (4) ACLs and
mechanisms for setting ACLs and
possible sector-specific ACLs in
relationship to the ABC, (5) ACT control
rule, (6) AMs and AM mechanisms, and
(7) stocks and stock complexes that have
statutory exceptions from ACLs or fall
under limited circumstances which
require different approaches to meet the
ACL requirements (e.g., ESA-listed
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stocks and harvests from aquaculture
facilities).
The Councils should evaluate the
extent to which their FMPs comply with
requirements to define MSY and OY for
stocks in the fishery, and the reasons
that OY is reduced from MSY (see
§ 600.310(e)(3)(iv) of this proposed
action). An overall objective of
management of federal fisheries under
the MSA is to conserve fishery resources
so as to prevent overfishing and achieve
OY (see sections 2(a)(6) and 2(b)(4) of
the MSA). OY is based on MSY for a
fishery, as reduced for economic, social,
or ecological reasons (see section
3(33)(B) of the MSA). Therefore, it is
important that all FMPs have MSY and
OY prescribed correctly.
FMPs should contain a description of
fisheries data for the stocks, stock
complexes, and ecosystem component
species. The sources of fishing
mortality, such as commercial catch
(both landed and discarded),
recreational catch, and bycatch in other
fisheries should be listed in the FMP for
each fishery, along with a description of
the data collection and estimation
methods used to quantify total catch
mortality in each fishery. The
description of the data collection
methods used to monitor the fishery
should include information on the
frequency that those data are collected
and updated and the scope of sampling
coverage for the fishery. In addition, the
FMP should describe how those data are
used to determine the relationship
between total catch at a given point in
time and the ACL for a stock or stock
complex.
FMPs should explain issues related to
shared jurisdiction of stocks (if any),
and the degree to which ACLs and AMs
established by the Councils will ensure
that overfishing does not occur on the
stock as a whole.
NMFS is aware that existing FMPs
may use terms that are similar to,
associated with, or may be equivalent to
ABC, ACL, ACT, and AM in many
fisheries for which annual specifications
are set for different stocks or stock
complexes. NMFS’ preference is that, as
Councils revise their FMPs, they use the
same terms as set forth in the NS1
guidelines as finalized. However, given
the longstanding use of terms under
certain FMPs, if changing terminology
could cause confusion, Councils could
opt to retain existing terminology and
explain in a proposed rule how the
terminology and approaches in the
FMPs are consistent with those set forth
in the NS1 guidelines.
Councils should amend their FMPs to
provide explicit narrative of how the
FMP objectives and annual management
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measures will work with ACLs and
AMs. All stocks and stock complexes
should have an annual or multiyear
specification process for stocks managed
in a fishery. An annual or multiyear
specification process for setting or
adjusting ACLs provides a timely,
consistent method that the public and
stakeholders can understand, and that
provides an opportunity for public
comment. Such a process could also
provide a method for assigning an ACL,
ACT, and AM to a ‘‘stock having a life
cycle of approximately one year’’ that is
undergoing overfishing.
XVIII. Change in Timetable When
Establishing a Rebuilding Plan
The MSA provides that the Secretary
shall annually identify stocks and stock
complexes that are overfished or
approaching a condition of being
overfished; notify the appropriate
Council at any time when a stock or
stock complex is determined to be
overfished; and notify the appropriate
Council when adequate progress is not
being made under existing FMPs, FMP
amendments, or regulations (see MSA
sections 304(e)(1), (2), and (7)). MSRA
did not change these identification and
notification provisions but revised the
timing of Council actions. Currently, the
Councils have 1 year to prepare an FMP,
an FMP amendment, or proposed
regulations (see MSA sections 304(e)(3)
and 304 note (Effective Date for
Subsection (c)). Beginning July 12, 2009,
the Councils have 2 years from the date
of an identification or notification to
prepare and implement an FMP, an
FMP amendment, or proposed
regulations ‘‘to end overfishing
immediately in the fishery and to
rebuild affected stocks * * * or to
prevent overfishing from occurring in
the fishery whenever such fishery is
identified as approaching an overfished
condition’’ (see MSA section 304(e)(3),
as revised by MSRA section 104(c)). To
facilitate timely implementation of
actions under revised section 304(e)(3),
the Councils should submit an FMP, an
FMP amendment, or proposed
regulations within 15 months of an
identification or notification under this
section. This will provide the Secretary
with 9 months to implement the
measures, if approved (see
§ 600.310(j)(2)(ii) of this proposed
action).
While MSA section 304(e)(3) provides
for two years for a Council to prepare
and implement an FMP, FMP
amendment, or proposed regulations, as
discussed earlier, MSA section
303(a)(15) has a separate requirement
for FMPs and ACLs that is effective in
fishing year 2010 for fisheries
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determined to be subject to overfishing
and in fishing year 2011 for all other
fisheries. Thus, as of 2010 and beyond,
for a stock and stock complex
determined to be overfished and
experiencing overfishing, a Council
needs to take measures consistent with
MSA section 303(a)(15) that address
overfishing while the rebuilding plan is
under development.
XIX. Establishing the Length of Time for
a Rebuilding Plan
NMFS proposes clarifying guidance
for calculating the target time to rebuild
(Ttarget) in rebuilding plans for stocks
(see § 600.310(j)(3)(i)(E) of this proposed
action), based on experiences with
FMPs since the last NS1 guideline
revisions. The purpose of this
clarification is to emphasize that the
rebuilding time must be ‘‘as short as
possible,’’ taking several factors into
account (see MSA section
304(e)(4)(A)(i)). Establishing the Ttarget
should be based on the minimum time
for rebuilding a stock (Tmin), and factors
described in § 600.310(j)(3) of this
proposed action with priority given to
rebuilding in as short a time as possible.
Ttarget shall not exceed the maximum
time allowable for rebuilding (Tmax) and
should generally be less than Tmax.
XX. Action When a Stock’s Rebuilding
Plan Ends and the Stock Is Not Rebuilt
Many rebuilding plans for overfished
stocks under section 304(e) of the MSA
were initiated in 1998, or later, and
some of those plans are reaching the end
of their rebuilding periods such that a
stock is no longer overfished, but not
rebuilt. NMFS does not have explicit
guidance in the NS1 guidelines to
describe what a Council should do
under such circumstances. Therefore,
NMFS proposes that if a stock reaches
the end of its rebuilding plan period and
it is not yet determined to be rebuilt,
then the rebuilding F should not be
increased until the stock has been
demonstrated to be rebuilt (see
§ 600.310(j)(3)(ii) of this proposed
action). If the rebuilding plan was based
on a Ttarget that was less than Tmax, and
the stock is not rebuilt by Ttarget,
rebuilding measures should be revised if
necessary, such that the stock will be
rebuilt by Tmax. If the stock has not
rebuilt by Tmax, and the rebuilding F is
greater than 75 percent of MFMT, then
the rebuilding F should be reduced to
no more than 75 percent of MFMT until
the stock has been demonstrated to be
rebuilt.
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XXI. Changes to the Definitions of Some
Components of MSY
NMFS is proposing changes to the
definitions of some components of
MSY. The purposes of these changes are
to improve some portions of the MSY
related definitions and to further clarify
how MSY is estimated. The definition of
MSY in the NS1 guidelines would
remain the same for the most part but
the phrase ‘‘and fishery technological
characteristics (e.g., gear selectivity) and
the distribution of catch among fleets’’
would be added to the end of the
definition (see § 600.310(e)(1)(i)(A) of
this proposed action). The purpose of
this change is to acknowledge that MSY
also depends upon gear selectivity (age
at entry) and the catch performance of
the fishery, which can depend on the
relative proportion of catch between
different fleets with differing fishing
characteristics. The definition of MSY
stock size would be changed in two
places. Currently, the guidelines state
that ‘‘MSY stock size means the longterm average size of the stock or stock
complex, measured in terms of
spawning biomass or other appropriate
units that would be achieved under a
MSY control rule in which the fishing
mortality rate is constant.’’ In the
proposed guidelines (see
§ 600.310(e)(1)(i)(C) of the proposed
action), NMFS clarifies that ‘‘other
appropriate units’’ means an
‘‘appropriate measure of the stock’s
reproductive potential.’’ NMFS also
replaces the statement that ‘‘the fishing
mortality rate is constant’’ with ‘‘Fmsy.’’
NMFS also added a definition for MSY
fishing mortality rate (Fmsy) (see
§ 600.310(e)(1)(i)(B) of the proposed
action), which was lacking in the
current guidelines. MSY fishing
mortality ‘‘is the fishing mortality rate
that, if applied over the long term,
would result in MSY.’’
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XXII. Social, Economic and Ecological
Factors as They Relate to OY
NMFS proposes additional guidance
to better describe social and ecological
factors, and minor revisions to the
economic factors as they relate to setting
OY for a stock (see § 600.310(e)(3)(iv) of
this proposed action). The revisions to
the social factors describe fisheryrelated indicators and non-fishery
related indicators that should be
considered when OY needs to be
reduced for a stock or stock complex.
XXIII. Scope of This Proposed Action
NMFS received voluminous
comments during its scoping comment
period for ACLs and AMs, including
proposals to strengthen guidance on
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ecosystem considerations when setting
ACLs and AMs. While NMFS has
carefully considered all comments
received, it will not be able to include
all proposed NS1 revisions in this
action. These proposed revisions to the
NS1 guidelines will address primarily
the need to have ACL and AM
mechanisms and ACLs and AMs in
place such that ACLs end overfishing in
2010, for stocks undergoing overfishing,
and prevent overfishing for all other
stocks beginning in 2011.
NMFS intends to withdraw most of
the proposed revisions to the NS1
guidelines that were published in 2005
in a separate withdrawal of a proposed
rule action. A few of the topics from the
2005 rule are considered in this action,
such as: (1) Establishing the length of
time for a rebuilding plan; (2) action to
take when a stock is not determined to
be rebuilt at the end of its rebuilding
plan; and (3) the definition of several
components of MSY. Other proposed
revisions considered in the 2005
proposed NS1 guidelines and suggested
during the comment period for this
action will be considered by NMFS for
possible inclusion in subsequent
revisions to the NS1 guidelines.
XXIV. Republishing Codified Text in Its
Entirety
For clarity and convenience of the
reader, this proposed rule would revise
§ 600.310 in its entirety. The following
describes the changes to § 600.310 that
are being proposed.
In the proposed revisions to
§ 600.310, paragraph (b)—General,
would be revised to contain a general
outline of information provided by the
NS1 guidelines. Current paragraph (b)
only contains a brief summary of the
relationship between MSY and OY.
Current paragraph (c)—MSY is revised
and redesignated paragraph (e)(1).
Current paragraph (d)(1)—Definitions,
is revised and redesignated paragraph
(e)(2)(i).
Current paragraph (d)(2)—
Specification of status determination
criteria, is revised and redesignated
paragraph (e)(2)(ii).
Current paragraph (d)(3)—
Relationship of status determination
criteria to other national standards is
revised, redesignated paragraph (l) and
renamed, ‘‘Relationship of National
Standard 1 to other national
standards.’’
Current paragraph (d)(6)—Exceptions,
is revised, redesignated paragraph (m),
and renamed, ‘‘Exceptions to
requirements to prevent overfishing.’’
Current paragraph (e)—Ending
overfishing and rebuilding overfished
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stocks, is revised and redesignated
paragraph (j)—Council actions to
address overfishing and rebuilding for
stocks and stock complexes in the
fishery.
Current paragraph (f)—OY is
redesignated paragraph (e)(3).
Revised paragraphs with much
different content include: Paragraph
(c)—Summary of Items to Include in
FMPs Related to NS1, paragraph (d)—
Classifying stocks in an FMP, and
paragraph (f)—Acceptable Biological
Catch, Annual Catch Limits, and
Annual Catch Targets.
New paragraphs that contain new
content not covered in the current NS1
guidelines include: (g) Accountability
measures, (h) Establishing ACL and AM
mechanisms in FMPs, (i) Fisheries data,
and (k) International overfishing.
XXV. Classification
Pursuant to the Magnuson-Stevens
Act, the NMFS Assistant Administrator
has determined that this proposed rule
is consistent with the MagnusonStevens Act, and other applicable law,
subject to further consideration after
public comment.
This proposed rule has been
determined to be significant for
purposes of Executive Order 12866.
NOAA has prepared a regulatory impact
review of this rulemaking, which is
available at: https://www.nmfs.noaa.gov/
msa2007/catchlimits.htm. This analysis
discusses various policy options that
NOAA considered in preparation of this
proposed rule, given NOAA’s
interpretation of the statutory terms in
the MSRA, such as the appropriate
meaning of the word ‘‘limit’’ in ‘‘Annual
Catch Limit,’’ and NOAA’s belief that it
has become necessary for Councils to
consider separately the uncertainties in
fishery management and the scientific
uncertainties in stock evaluation in
order to effectively set fishery
management policies and ensure
fulfillment of the goals to end
overfishing and rebuild overfished
stocks.
NOAA invites the public to comment
on this proposal, the supporting
analysis, and its underlying
interpretation of the analytical
requirements of the MSRA. In
particular, NOAA seeks comment on:
The appropriate interplay of the OFL,
ABC, ACL and ACT; whether the
Council’s experience with MSY and OY
would readily translate into these new
concepts; whether the ACT and ACT
control rules, as proposed, would be
effective tools in managing fisheries at
risk; the degree to which Councils
should have the flexibility to specify
stringent AMs to prevent the ACL from
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being exceeded in lieu of setting an ACT
and ACT control rules; and the expected
burden of these analytical requirements,
both in terms of time and resources.
The Chief Counsel for Regulation of
the Department of Commerce certified
to the Chief Counsel for Advocacy of the
Small Business Administration that
these proposed revisions to the NS1
guidelines, if adopted, would not have
any significant economic impact on a
substantial number of small entities, as
follows:
I certify that the attached proposed action
issued under the authority of the MagnusonStevens Fishery Conservation and
Management Act (MSA) will not have any
significant economic impacts on a substantial
number of small entities, as defined under
the Regulatory Flexibility Act. The proposed
action would revise the National Standard 1
(NS1) guidelines at 50 CFR 600.310.
The proposed revisions to the NS1
guidelines provide guidance on how to
address new overfishing and rebuilding and
related requirements under MSA sections
303(a)(15), 304(e), and other sections.
Pursuant to section 301(b) of the Act, the NS
guidelines do not have the force and effect
of law. Regional Fishery Management
Councils (Councils) and the Secretary of
Commerce would use the NS1 guidelines
when developing or amending FMPs to
implement annual catch limits (ACLs) and
accountability measures (AMs) and to take
necessary actions to rebuild overfished
fisheries. ACL and AM requirements under
section 303(a)(15) of the Magnuson-Stevens
Act are effective in fishing year 2010, for
stocks undergoing overfishing and in fishing
year 2011, for all other fisheries. NMFS
believes that revisions to the NS1 guidelines
will assist the Councils and the Secretary in
addressing new MSA requirements, ensure
greater consistency in approaches to ending
overfishing and rebuilding stocks, increase
efficiency in reviewing actions and tracking
annual management performance, and
improve communication between NMFS and
the Councils.
Because the NS1 guidelines are general
guidance and there is considerable diversity
in the different federally-managed fisheries,
potential economic impacts of the guidelines
are highly speculative. As the Councils and/
or the Secretary apply these guidelines to
specific fisheries, they will develop FMPs,
FMP amendments, or other regulatory actions
that will be accompanied by environmental,
economic, and social analyses prepared
pursuant to the Regulatory Flexibility Act,
National Environmental Policy Act, and
other statutes.
NMFS has identified a total of 59,823
commercial vessel permit holders and 18,486
headboat and charter boat vessel permits. A
total of 26,074 recreational permits exist for
Atlantic highly migratory species (HMS).
Operator permits are estimated at 6,636 and
dealer permits were estimated at 7,550.
However, it is important to note that in most
cases each vessel possesses permits for
several fisheries (multiple vessel permits). As
such, the total number of vessel permits
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(commercial, headboat and charter boat, and
HMS recreational) grossly overestimate the
actual number of vessels that are operating in
these fisheries. All vessels included in the
total vessel permits for each fishery are
considered to be small entities for the
purposes of the Regulatory Flexibility Act
analysis. As a result, NMFS does not believe
that these proposed revisions to the NS1
guidelines would place a substantial number
of small entities at a disadvantage as
compared to large entities or that it would
reduce profit significantly. The NS1
guidelines would provide general guidance
on ending and preventing overfishing and
rebuilding fisheries, leaving considerable
discretion to the Councils and the Secretary
to consider alternative ways to accomplish
these goals consistent with the NS, other
provisions of the Magnuson-Stevens Act, and
other applicable law. Therefore, an IRFA has
not been prepared for this action.
These proposed revisions to the NS1
guidelines do not contain any new
recordkeeping or reporting requirements
subject to the Paperwork Reduction Act.
When the Councils and the Secretary develop
FMPs, FMP amendments, or other regulatory
actions per the Magnuson-Stevens Act and
NS1 guidelines, such actions may include
new proposed collection-of-information
requirements. In the event that new
collection-of-information requirements are
proposed, a specific analysis regarding the
public’s reporting burden would accompany
such action. NMFS is not aware of any other
relevant federal rules that may duplicate,
overlap or conflict with the proposed rule.
List of Subjects in 50 CFR Part 600
Fisheries, Fishing, Reporting and
recordkeeping requirements.
Dated: June 3, 2008.
Samuel D. Rauch, III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
For the reasons stated in the
preamble, 50 CFR part 600 is proposed
to be amended as follows:
PART 600—MAGNUSON-STEVENS
ACT PROVISIONS
1. The authority citation for part 600
continues to read as follows:
Authority: 16 U.S.C. 1801 et seq.
2. Section 600.310 is revised to read
as follows:
§ 600.310
Yield.
National Standard 1—Optimum
(a) Standard 1. Conservation and
management measures shall prevent
overfishing while achieving, on a
continuing basis, the optimum yield
(OY) from each fishery for the U.S.
fishing industry.
(b) General. (1) The guidelines set
forth in this section describe fishery
management approaches to meet the
objectives of National Standard 1 (NS1),
and include guidance on:
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(i) Specifying maximum sustainable
yield (MSY) and OY;
(ii) Specifying status determination
criteria (SDC) so that overfishing and
overfished determinations can be made
for stocks and stock complexes that are
part of a fishery;
(iii) Preventing overfishing and
achieving OY using a system of limits
and targets, incorporation of scientific
and management uncertainty in control
rules, and adaptive management using
annual catch limits (ACL) and measures
to ensure accountability (AM); and
(iv) Rebuilding stocks and stock
complexes.
(2) Overview of Magnuson-Stevens
Act concepts and provisions related to
NS1—(i) MSY. The Magnuson-Stevens
Act establishes MSY as the basis for
fishery management and requires that:
The fishing mortality rate does not
jeopardize the capacity of a stock or
stock complex to produce MSY; the
abundance of an overfished stock or
stock complex be rebuilt to a level that
is capable of producing MSY; and OY
not exceed MSY.
(ii) OY. The determination of OY is a
decisional mechanism for resolving the
Magnuson-Stevens Act’s conservation
and management objectives, achieving a
fishery management plan’s (FMP)
objectives, and balancing the various
interests that comprise the greatest
overall benefits to the Nation. OY is
based on MSY as reduced under
paragraphs (e)(3)(iii) and (iv) of this
section. The most important limitation
on the specification of OY is that the
choice of OY and the conservation and
management measures proposed to
achieve it must prevent overfishing.
(iii) ACLs and AMs. Any FMP which
is prepared by any Council shall
establish a mechanism for specifying
ACLs in the FMP (including a multiyear
plan), implementing regulations, or
annual specifications, at a level such
that overfishing does not occur in the
fishery, including measures to ensure
accountability (Magnuson-Stevens Act
section 303(a)(15)). Subject to certain
exceptions and circumstances described
in paragraph (h) of this section, this
requirement takes effect in fishing year
2010, for fisheries determined subject to
overfishing, and in fishing year 2011 for
all other fisheries (Magnuson-Stevens
Act section 303 note). ‘‘Council’’
includes the Regional Fishery
Management Councils and the Secretary
of Commerce, as appropriate (see
§ 600.305(c)(11)).
(iv) Reference points. SDC, MSY,
acceptable biological catch (ABC), ACL,
and annual catch target (ACT), which
are described further in paragraphs (e)
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and (f) of this section, are collectively
referred to as ‘‘reference points.’’
(v) Scientific advice. The MagnusonStevens Act has requirements regarding
scientific and statistical committees
(SSC) of the Regional Fishery
Management Councils, including but
not limited to, the following provisions:
(A) Each Regional Fishery
Management Council shall establish an
SSC as described in section 302(g)(1)(A)
of the Magnuson-Stevens Act.
(B) Each SSC shall provide its
Regional Fishery Management Council
recommendations for ABC as well as
other scientific advice, as described in
Magnuson-Stevens Act section
302(g)(1)(B). The SSC may specify the
type of information that should be
included in the Stock Assessment and
Fishery Evaluation (SAFE) report (see
§ 600.315).
(C) The Secretary and each Regional
Fishery Management Council may
establish a peer review process for that
Regional Fishery Management Council
for scientific information used to advise
the Regional Fishery Management
Council about the conservation and
management of the fishery (see
Magnuson-Stevens Act section
302(g)(1)(E)). If a peer review process is
established, it should investigate the
technical merits of stock assessments
and other scientific information used by
the SSC. The peer review process is not
a substitute for the SSC and should
work in conjunction with the SSC.
(D) Each Regional Fishery
Management Council shall develop
ACLs for each of its managed fisheries
that may not exceed the fishing level
recommendations of its SSC or peer
review process (Magnuson-Stevens Act
section 302(h)(6)).
(3) Approach for setting limits and
targets for consistency with NS1. In
general, when specifying limits and
targets intended to avoid overfishing
and achieve sustainable fisheries,
Councils should take an approach that
considers uncertainty in scientific
information and management control of
the fishery. These guidelines identify
limit and target reference points which
should be set lower as uncertainty
increases such that there is a low risk
that limits are exceeded as described in
paragraphs (f)(4) and (f)(6) of this
section.
(c) Summary of items to include in
FMPs related to NS1. This section
provides a summary of items that
Councils should include in their FMPs
and FMP amendments in order to
address ACL, AM, and other aspects of
the NS1 guidelines. As described in
further detail in paragraphs (c)(1)
through (7) of this section, Councils may
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review their FMPs to decide if all stocks
are ‘‘in the fishery’’ or whether some fit
the category of ‘‘ecosystem component
species’’ and amend their FMPs as
appropriate. If they do not establish
ecosystem component species through
an FMP amendment, then all stocks in
an FMP are presumed to be ‘‘in the
fishery.’’ Councils should also describe
fisheries data for the stocks, stock
complexes, and ecosystem component
species in their FMPs. For all stocks and
stock complexes that are ‘‘in the
fishery,’’ the Councils should evaluate
and describe the following items in their
FMPs and amend the FMPs, if
necessary, to align their management
objectives to end or prevent overfishing:
(1) MSY and SDC (see paragraphs
(e)(1) and (2) of this section).
(2) OY at the stock, stock complex, or
fishery level and provide the OY
specification analysis (see paragraph
(e)(3) of this section).
(3) ABC control rule (see paragraph
(f)(4) of this section).
(4) ACLs and mechanisms for setting
ACLs and possible sector-specific ACLs
in relationship to the ABC (see
paragraphs (f)(5) and (h) of this section).
(5) ACT control rule (see paragraph
(f)(6) of this section).
(6) AMs and AM mechanisms (see
paragraphs (g) and (h)(1) of this section).
(7) Stocks and stock complexes that
have statutory exceptions from ACLs
(see paragraph (h)(2) of this section) or
which fall under limited circumstances
which require different approaches to
meet the ACL requirements (see
paragraph (h)(3) of this section).
(d) Classifying stocks in an FMP—(1)
Introduction. Magnuson-Stevens Act
section 303(a)(2) requires that an FMP
contain, among other things, a
description of the species of fish
involved in the fishery. FMPs include
target stocks and may also include nontarget species or stocks. All stocks listed
in an FMP or FMP amendment are
considered to be ‘‘in the fishery’’ unless
they are identified as ecosystem
component (EC) species through an
FMP amendment process.
(2) Stocks in a fishery. Stocks in a
fishery include: Target stocks; nontarget stocks that are retained for sale or
personal use; and non-target stocks that
are not retained for sale or personal use
and that are either determined to be
subject to overfishing, approaching
overfished, or overfished, or could
become so, according to the best
available information, without
conservation and management
measures. Stocks in a fishery may be
grouped into stock complexes, as
appropriate. Requirements for reference
points and management measures for
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these stocks are described throughout
these guidelines.
(3) ‘‘Target stocks’’ are stocks that
fishers seek to catch for sale or personal
use, including ‘‘economic discards’’ as
defined under Magnuson-Stevens Act
section 3(9).
(4) ‘‘Non-target species’’ and ‘‘nontarget stocks’’ are fish caught
incidentally during the pursuit of target
stocks in a fishery, including
‘‘regulatory discards’’ as defined under
Magnuson-Stevens Act section 3(38).
They may or may not be retained for
sale or personal use. Non-target species
may be included in a fishery and, if so,
they should be identified at the stock
level. Some non-target species may be
identified in an FMP as ecosystem
component (EC) species or stocks.
(5) ‘‘Ecosystem component (EC)
species’’ are generally not retained for
any purpose, although de minimis
amounts might occasionally be retained.
EC species may be identified at the
species or stock level, and may be
grouped into complexes. EC species
may be included in an FMP or FMP
amendment for any of the following
reasons: For data collection purposes;
for ecosystem considerations related to
specification of OY for the associated
fishery; as considerations in the
development of conservation and
management measures for the associated
fishery; and/or to address other
ecosystem issues. While EC species are
not considered to be ‘‘in the fishery,’’ a
Council should consider measures for
the fishery to minimize bycatch and
bycatch mortality of EC species
consistent with National Standard 9,
and to protect their associated role in
the ecosystem. EC species do not require
specification of reference points but
should be monitored on a regular basis,
to the extent practicable, to determine
changes in their status or their
vulnerability to the fishery. If necessary,
they should be reclassified as ‘‘in the
fishery.’’
(6) Reclassification. A Council should
monitor the catch resulting from a
fishery on a regular basis to determine
if the stocks and species are
appropriately classified in the FMP. If
the criteria previously used to classify a
stock or species is no longer valid, the
Council should reclassify it through an
FMP amendment, which documents
rationale for the decision.
(7) Stocks or species identified in
more than one FMP. If a stock is
identified in more than one fishery,
Councils should choose which FMP will
be the primary FMP in which
management objectives, SDC, and other
reference points for the stock are
established. In most cases, the primary
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FMP for a stock will be the one in which
the stock is identified as a target stock.
Other FMPs in which the stock is
identified as part of a fishery should be
consistent with the primary FMP.
(8) Stock complex. ‘‘Stock complex’’
means a group of stocks that are
sufficiently similar in geographic
distribution, life history, and
vulnerabilities to the fishery such that
the impact of management actions on
the stocks is similar. Stocks may be
grouped into complexes for various
reasons, including where stocks in a
multispecies fishery cannot be targeted
independent of one another; where
there is insufficient data to measure
their status relative to SDC; or when it
is not feasible for fishermen to
distinguish individual stocks among
their catch. The vulnerability of stocks
to the fishery should be evaluated when
determining if a particular stock
complex should be established or
reorganized, or if a particular stock
should be included in a complex. Stock
complexes may be comprised of: One or
more indicator stocks, each of which
has SDC and ACLs, and several other
stocks; several stocks without an
indicator stock, with SDC and an ACL
for the complex as a whole; or one of
more indicator stocks, each of which
has SDC and management objectives,
with an ACL for the complex as a whole
(this situation might be applicable to
some salmon species).
(9) Indicator stocks. An indicator
stock is a stock that is used to help
manage and evaluate stocks that are in
a stock complex and do not have their
own SDC. If an indicator stock is used
to evaluate the status of a complex, it
should be representative of the typical
status of each stock within the complex,
due to similarity in vulnerability. If the
stocks within a stock complex have a
wide range of vulnerability, they should
be reorganized into different stock
complexes that have similar
vulnerabilities; otherwise the indicator
stock should be chosen to represent the
more vulnerable stocks within the
complex. In instances where an
indicator stock is less vulnerable than
other members of the complex,
management measures need to be more
conservative so that the more vulnerable
members of the complex are not at risk
from the fishery. More than one
indicator stock can be selected to
provide more information about the
status of the complex. Although the
indicator stock(s) are used to evaluate
the status of the complex, individual
stocks within complexes should be
examined periodically using available
quantitative or qualitative information
to evaluate whether a stock has become
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overfished or may be subject to
overfishing.
(e) Features of MSY, SDC, and OY
that should be identified in FMPs for all
stocks and stock complexes in the
fishery—(1) MSY. Each FMP should
include an estimate of MSY for the
stocks and stock complexes in the
fishery, as described in paragraph (d)(2)
of this section).
(i) Definitions. (A) MSY is the largest
long-term average catch or yield that can
be taken from a stock or stock complex
under prevailing ecological,
environmental conditions and fishery
technological characteristics (e.g., gear
selectivity), and the distribution of catch
among fleets.
(B) MSY fishing mortality rate (Fmsy) is
the fishing mortality rate that, if applied
over the long term, would result in
MSY.
(C) MSY stock size (Bmsy) means the
long-term average size of the stock or
stock complex, measured in terms of
spawning biomass or other appropriate
measure of the stock’s reproductive
potential that would be achieved by
fishing at Fmsy.
(ii) MSY for stocks. MSY should be
estimated for each stock based on the
best scientific information available (see
§ 600.315).
(iii) MSY for stock complexes. MSY
should be estimated on a stock-by-stock
basis whenever possible. However,
where MSY cannot be estimated for
each stock in a stock complex, then
MSY may be estimated for one or more
indicator stocks for the complex or for
the complex as a whole. When indicator
stocks are used, the stock complex’s
MSY could be listed as ‘‘unknown,’’
while noting that the complex is
managed on the basis of one or more
indicator stocks that do have known,
stock-specific MSYs or suitable proxies
as described in paragraph (e)(1)(iv) of
this section. When indicator stocks are
not used, MSY or a suitable proxy
should be calculated for the stock
complex as a whole.
(iv) Specifying MSY. Because MSY is
a long-term average, it need not be
estimated annually, but it must be based
on the best scientific information
available (see § 600.315), and should be
re-estimated as required by changes in
long-term environmental or ecological
conditions, fishery technological
characteristics, or new scientific
information. When data are insufficient
to estimate MSY directly, Councils
should adopt other measures of
reproductive potential, based on the
best scientific information available,
that can serve as reasonable proxies for
MSY, Fmsy, and Bmsy, to the extent
possible. As MSY values are estimates
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and will have some level of uncertainty
associated with them, the degree of
uncertainty in the estimates should be
identified, when possible, through the
stock assessment process and peer
review (see § 600.335).
(2) Status determination criteria—(i)
Definitions—(A) Status determination
criteria (SDC) mean the quantifiable
factors, MFMT, OFL, and MSST, or their
proxies, that are used to determine if
overfishing has occurred, or if the stock
or stock complex is overfished.
Magnuson-Stevens Act (section 3(34))
defines both ‘‘overfishing’’ and
‘‘overfished’’ to mean a rate or level of
fishing mortality that jeopardizes the
capacity of a fishery to produce the
MSY on a continuing basis. To avoid
confusion, this section clarifies that
‘‘overfished’’ relates to biomass of a
stock or stock complex, and
‘‘overfishing’’ pertains to a rate or level
of removal of fish from a stock or stock
complex.
(B) Overfishing (to overfish) occurs
whenever a stock or stock complex is
subjected to a level of fishing mortality
or annual total catch that jeopardizes
the capacity of a stock or stock complex
to produce MSY on a continuing basis.
(C) Maximum fishing mortality
threshold (MFMT) means the level of
fishing mortality (F), on an annual basis,
above which overfishing is occurring.
(D) Overfishing limit (OFL) means the
annual amount of catch that
corresponds to the estimate of MFMT
applied to a stock or stock complex’s
abundance and is expressed in terms of
numbers or weight of fish. MSY is the
long-term average of such catches.
(E) Overfished. A stock or stock
complex is considered ‘‘overfished’’
when its biomass has declined below a
level that jeopardizes the capacity of the
stock or stock complex to produce MSY
on a continuing basis.
(F) Minimum stock size threshold
(MSST) means the level of biomass
below which the stock or stock complex
is considered to be overfished.
(G) Approaching an overfished
condition. A stock or stock complex is
approaching an overfished condition
when it is projected that there is more
than a 50 percent chance that the
biomass of the stock or stock complex
will decline below the MSST within
two years.
(ii) Specification of SDC and
overfishing and overfished
determinations. SDC must be expressed
in a way that enables the Council to
monitor each stock or stock complex in
the FMP and determine annually, if
possible, whether overfishing is
occurring and whether the stock or
stock complex is overfished. In
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specifying SDC, a Council should
provide an analysis of how the SDC
were chosen and how they relate to
reproductive potential. Each FMP must
specify, to the extent possible, objective
and measurable SDC as follows (see
paragraphs (e)(2)(ii)(A) and (B) of this
section):
(A) SDC to determine overfishing
status. Each FMP should describe which
of the following two methods will be
used for each stock or stock complex to
determine an overfishing status.
(1) Fishing mortality rate exceeds
MFMT. Exceeding the MFMT for a
period of 1 year or more constitutes
overfishing. The MFMT or reasonable
proxy may be expressed either as a
single number (a fishing mortality rate
or F value), or as a function of spawning
biomass or other measure of
reproductive potential. The MFMT must
not exceed Fmsy.
(2) Catch exceeds the OFL. Should the
annual catch exceed the annual OFL for
1 year or more, the stock or stock
complex is considered subject to
overfishing.
(B) SDC to determine overfished
status. The MSST or reasonable proxy
should be expressed in terms of
spawning biomass or other measure of
reproductive potential. To the extent
possible, the MSST should equal
whichever of the following is greater:
One-half the MSY stock size, or the
minimum stock size at which rebuilding
to the MSY level would be expected to
occur within 10 years if the stock or
stock complex were exploited at the
MFMT specified under paragraph
(e)(2)(ii)(A)(1) of this section. Should
the estimated size of the stock or stock
complex in a given year fall below this
threshold, the stock or stock complex is
considered overfished.
(iii) Relationship of SDC to
environmental change. Some short-term
environmental changes can alter the size
of a stock or stock complex without
affecting its long-term reproductive
potential. Long-term environmental
changes affect both the short-term size
of the stock or stock complex and the
long-term reproductive potential of the
stock or stock complex.
(A) If environmental changes cause a
stock or stock complex to fall below its
MSST without affecting its long-term
reproductive potential, fishing mortality
must be constrained sufficiently to
allow rebuilding within an acceptable
time frame (also see paragraph (j)(3)(ii)
of this section). SDC should not be
respecified.
(B) If environmental changes affect
the long-term reproductive potential of
the stock or stock complex, one or more
components of the SDC must be
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respecified. Once SDC have been
respecified, fishing mortality may or
may not have to be reduced, depending
on the status of the stock or stock
complex with respect to the new
criteria.
(C) If manmade environmental
changes are partially responsible for a
stock or stock complex being in an
overfished condition, in addition to
controlling fishing mortality, Councils
should recommend restoration of
habitat and other ameliorative programs,
to the extent possible (see also the
guidelines issued pursuant to section
305(b) of the Magnuson-Stevens Act for
Council actions concerning essential
fish habitat).
(iv) Secretarial approval of SDC.
Secretarial approval or disapproval of
proposed SDC will be based on
consideration of whether the proposal:
(A) Has sufficient scientific merit;
(B) Contains the elements described
in paragraph (e)(2)(ii) of this section;
(C) Provides a basis for objective
measurement of the status of the stock
or stock complex against the criteria;
and
(D) Is operationally feasible.
(3) Optimum yield—(i) Definitions—
(A) Optimum yield (OY). MagnusonStevens Act section 3(33) defines
‘‘optimum,’’ with respect to the yield
from a fishery, as 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;
that is prescribed on the basis of the
MSY from the fishery, as reduced by
any relevant economic, social, or
ecological factor; and, in the case of an
overfished fishery, that provides for
rebuilding to a level consistent with
producing the MSY in such fishery. OY
may be established at the stock or stock
complex level, or at the fishery level.
(B) In NS1, use of the phrase
‘‘achieving, on a continuing basis, the
optimum yield from each fishery’’
means producing, from each stock, stock
complex, or fishery: A long-term series
of catches such that the average catch is
equal to the OY, overfishing is
prevented, the long term average
biomass is near or above Bmsy, and
overfished stocks and stock complexes
are rebuilt consistent with timing and
other requirements of section 304(e)(4)
of the Magnuson-Stevens Act and
paragraph (j) of this section.
(ii) General. OY is a long-term average
amount of desired yield from a stock,
stock complex, or fishery. The long-term
objective is to achieve OY through
annual achievement of ACT, which is
described in paragraph (f) of this
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section. An FMP must contain
conservation and management measures
to achieve OY, and provisions for
information collection that are designed
to determine the degree to which OY is
achieved on a continuing basis—that is,
to result in a long-term average catch
equal to the long-term average OY,
through an effective system of ACLs,
ACTs, and AMs. These measures should
allow for practical and effective
implementation and enforcement of the
management regime. The Secretary has
an obligation to implement and enforce
the FMP. If management measures prove
unenforceable—or too restrictive, or not
rigorous enough to prevent overfishing
while achieving OY—they should be
modified; an alternative is to reexamine
the adequacy of the OY specification.
Exceeding OY does not necessarily
constitute overfishing. However, even if
no overfishing resulted from exceeding
OY, continual harvest at a level above
OY would violate NS1, because OY was
not achieved on a continuing basis. An
FMP must contain an assessment and
specification of OY, including a
summary of information utilized in
making such specification, consistent
with requirements of section 303(a)(3) of
the Magnuson-Stevens Act. A Council
must identify those economic, social,
and ecological factors relevant to
management of a particular stock, stock
complex, or fishery, then evaluate them
to determine the OY. The choice of a
particular OY must be carefully
documented to show that the OY
selected will produce the greatest
benefit to the Nation and prevent
overfishing.
(iii) Determining the greatest benefit
to the Nation. In determining the
greatest benefit to the Nation, the values
that should be weighed and receive
serious attention when considering the
economic, social, or ecological factors
used in reducing MSY to obtain OY are:
(A) The benefits of food production
are derived from providing seafood to
consumers; maintaining an
economically viable fishery together
with its attendant contributions to the
national, regional, and local economies;
and utilizing the capacity of the
Nation’s fishery resources to meet
nutritional needs.
(B) The benefits of recreational
opportunities reflect the quality of both
the recreational fishing experience and
non-consumptive fishery uses such as
ecotourism, fish watching, and
recreational diving. Benefits also
include the contribution of recreational
fishing to the national, regional, and
local economies and food supplies.
(C) The benefits of protection afforded
to marine ecosystems are those resulting
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from maintaining viable populations
(including those of unexploited
species), maintaining adequate forage
for all components of the ecosystem,
maintaining evolutionary and ecological
processes (e.g., disturbance regimes,
hydrological processes, nutrient cycles),
maintaining the evolutionary potential
of species and ecosystems, and
accommodating human use.
(iv) Factors to consider in OY
specification. Because fisheries have
limited capacities, any attempt to
maximize the measures of benefits
described in paragraph (e)(3)(iii) of this
section will inevitably encounter
practical constraints. OY cannot exceed
MSY in any circumstance and must take
into account the need to prevent
overfishing and rebuild overfished
stocks and stock complexes. OY can be
reduced to a value less than MSY based
on social, economic, and ecological
factors. To the extent possible, the
relevant social, economic, and
ecological factors used to establish OY
for a stock, stock complex, or fishery
should be quantified and reviewed in
historical, short-term, and long-term
contexts. Even where quantification of
these factors is not possible, the FMP
still must address these factors in its OY
specification.
(A) Social factors. Examples are
enjoyment gained from recreational
fishing, avoidance of gear conflicts and
resulting disputes, preservation of a way
of life for fishermen and their families,
and dependence of local communities
on a fishery (e.g., involvement in
fisheries and ability to adapt to change).
Consideration may be given to fisheryrelated indicators (e.g., number of
fishery permits, number of commercial
fishing vessels, number of party and
charter trips, landings, ex-vessel
revenues etc.) and non-fishery related
indicators (e.g., unemployment rates,
percent of population below the poverty
level, population density, etc.). Other
factors that may be considered include
the effects that past harvest levels have
had on fishing communities, the
cultural place of subsistence fishing,
obligations under Indian treaties,
proportions of affected minority and
low-income groups, and worldwide
nutritional needs.
(B) Economic factors. Examples are
prudent consideration of the risk of
overharvesting when a stock’s size or
reproductive potential is uncertain (see
§ 600.335(c)(2)(i)), satisfaction of
consumer and recreational needs, and
encouragement of domestic and export
markets for U.S. harvested fish. Other
factors that may be considered include
the value of fisheries, the level of
capitalization, the decrease in cost per
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unit of catch afforded by an increase in
stock size, the attendant increase in
catch per unit of effort, alternate
employment opportunities, and
economic contribution to fishing
communities, coastal areas, affected
states, and the nation.
(C) Ecological factors. Examples
include impacts on ecosystem
component species, forage fish stocks,
other fisheries, predator-prey or
competitive interactions, marine
mammals, threatened or endangered
species, and birds. Species interactions
that have not been explicitly taken into
account when calculating MSY should
be considered as relevant factors for
setting OY below MSY. In addition,
consideration should be given to
managing forage stocks for higher
biomass than Bmsy to enhance and
protect the marine ecosystem. Also
important are ecological or
environmental conditions that stress
marine organisms, such as natural and
manmade changes in wetlands or
nursery grounds, and effects of
pollutants on habitat and stocks.
(v) Specification of OY. The
specification of OY must be consistent
with preventing overfishing and should
be reduced from MSY to account for
scientific uncertainty in calculating
MSY, and economic, social, and
ecological factors such as those
described in paragraph (e)(3)(iv) of this
section. If the estimates of MFMT and
current biomass are known with a high
level of certainty and management
controls can accurately limit catch to
the ACT then OY could be set very close
to MSY. To the degree that such MSY
estimates and management controls are
lacking or unavailable, OY should be set
farther from MSY. In order to achieve
OY in the long term, catch targets (i.e.,
ACT) should be set below catch limits
(i.e., ACLs) based on the degree of
management control so that average
catch (or average ACT) approximates
OY (see paragraph (f)(6) of this section).
If management measures cannot
adequately control fishing mortality so
that the specified OY can be achieved
without overfishing, the Council should
reevaluate the management measures
and specification of OY so that the dual
requirements of NS1 (preventing
overfishing while achieving, on a
continuing basis, OY) are met.
(A) The amount of fish that
constitutes the OY should be expressed
in terms of numbers or weight of fish.
As a long-term average, OY cannot
exceed MSY.
(B) Either a range or a single value
may be specified for OY. Specification
of a numerical, fixed-value OY does not
preclude use of ACTs that vary with
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stock size or management precision. For
example, an ACT control rule (described
in paragraph (f)(6) of this section) might
prescribe a smaller ACT if there is less
management precision.
(C) All catch must be counted against
OY, including that resulting from
bycatch, scientific research, and all
fishing activities.
(D) The OY specification should be
translatable into an annual numerical
estimate for the purposes of establishing
any total allowable level of foreign
fishing (TALFF) and analyzing impacts
of the management regime.
(E) The determination of OY is based
on MSY, directly or through proxy.
However, even where sufficient
scientific data as to the biological
characteristics of the stock do not exist,
or where the period of exploitation or
investigation has not been long enough
for adequate understanding of stock
dynamics, or where frequent large-scale
fluctuations in stock size diminish the
meaningfulness of the MSY concept, OY
must still be established based on the
best scientific information available.
(F) An OY established at a fishery
level may not exceed the sum of the
MSY values for each of the stocks or
stock complexes within the fishery. If
OY is specified at a fishery level, the
sum of the ACTs for the stocks and
stock complexes in the fishery should
approximate OY.
(G) There should be a mechanism in
the FMP for periodic reassessment of
the OY specification, so that it is
responsive to changing circumstances in
the fishery.
(H) Part of the OY may be held as a
reserve to allow for factors such as
uncertainties in estimates of stock size
and domestic annual harvest (DAH). If
an OY reserve is established, an
adequate mechanism should be
included in the FMP to permit timely
release of the reserve to domestic or
foreign fishermen, if necessary.
(vi) OY and foreign fishing. Section
201(d) of the Magnuson-Stevens Act
provides that fishing by foreign nations
is limited to that portion of the OY that
will not be harvested by vessels of the
United States. The FMP must include an
assessment to address the following, as
required by section 303(a)(4) of the
Magnuson-Stevens Act:
(A) DAH. Councils and/or the
Secretary must consider the capacity of,
and the extent to which, U.S. vessels
will harvest the OY on an annual basis.
Estimating the amount that U.S. fishing
vessels will actually harvest is required
to determine the surplus.
(B) Domestic annual processing
(DAP). Each FMP must assess the
capacity of U.S. processors. It must also
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assess the amount of DAP, which is the
sum of two estimates: The estimated
amount of U.S. harvest that domestic
processors will process, which may be
based on historical performance or on
surveys of the expressed intention of
manufacturers to process, supported by
evidence of contracts, plant expansion,
or other relevant information; and the
estimated amount of fish that will be
harvested by domestic vessels, but not
processed (e.g., marketed as fresh whole
fish, used for private consumption, or
used for bait).
(C) Joint venture processing (JVP).
When DAH exceeds DAP, the surplus is
available for JVP.
(f) Acceptable biological catch,
annual catch limits, and annual catch
targets. The following features (see
paragraphs (f)(1) through (f)(7) of this
section) of acceptable biological catch,
annual catch limits, and annual catch
targets apply to stocks and stock
complexes in the fishery (see paragraph
(d)(2) of this section).
(1) Introduction. A control rule is a
policy for establishing a limit or target
fishing level that is based on the best
available scientific information and is
established by fishery managers in
consultation with fisheries scientists.
Control rules should be designed so that
management actions become more
conservative as biomass estimates, or
other proxies, for a stock or stock
complex decline and as science and
management uncertainty increases.
Paragraph (f) of this section describes a
three-step approach for setting limits
and targets so as to ensure a low risk of
overfishing while achieving, on a
continuing basis, OY: First, ABC is set
below the OFL to account for scientific
uncertainty in calculating the OFL;
second, ACL is set at an amount not to
exceed the ABC; and third, ACT is set
at an amount not to exceed the ACL to
account for management uncertainty in
controlling a fishery’s actual catch.
(2) Definitions. (i) Catch is the total
quantity of fish, measured in weight or
numbers of fish, taken in commercial,
recreational, subsistence, tribal, and
other fisheries. Catch includes fish that
are retained for any purpose, as well as
mortality of fish that are discarded.
(ii) Acceptable biological catch (ABC)
is a level of a stock or stock complex’s
annual catch that accounts for the
scientific uncertainty in the estimate of
OFL and should be specified based on
the ABC control rule.
(iii) ABC control rule means a
specified approach to setting the ABC
for a stock or stock complex as a
function of the scientific uncertainty in
the estimate of OFL.
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(iv) Annual catch limit (ACL) is the
level of annual catch of a stock or stock
complex that serves as the basis for
invoking AMs. ACL cannot exceed the
ABC, but may be divided into sectorACLs (see paragraph (f)(5) of this
section).
(v) Annual catch target (ACT) is an
amount of annual catch of a stock or
stock complex that is the management
target of the fishery. A stock or stock
complex’s ACT should usually be less
than its ACL and results from the
application of the ACT control rule. If
sector-ACLs have been established, each
one should have a sector-ACT.
(vi) ACT control rule means a
specified approach to setting the ACT
for each stock or stock complex such
that the risk of exceeding the ACL due
to management uncertainty is at an
acceptably low level.
(3) Specification of ABC. ABC may
not exceed OFL (see paragraph
(e)(2)(i)(D) of this section) and is
recommended to be reduced from OFL
to account for scientific uncertainty in
the estimate of OFL. Councils should
develop a process for receiving
scientific information and advice used
to establish ABC. This process should:
Establish an ABC control rule, identify
the body that will apply the ABC
control rule (i.e., calculates the ABC),
identify the review process that will
verify the resulting ABC, and confirm
that the SSC recommends the ABC to
the Council. For Secretarial FMPs or
FMP amendments, agency scientists or
a peer review process would provide the
scientific advice to establish ABC. For
internationally-assessed stocks, an ABC
as defined in these guidelines is not
required.
(i) Expression of ABC. ABC should be
expressed in terms of catch, but may be
expressed in terms of landings as long
as estimates of bycatch and any other
fishing mortality not accounted for in
the landings are incorporated into the
determination of ABC.
(ii) ABC for overfished stocks. For
overfished stocks and stock complexes,
a rebuilding ABC must be set to reflect
the annual catch that is consistent with
the target fishing mortality rates in the
rebuilding plan.
(4) ABC control rule. For stocks and
stock complexes required to have an
ABC, each Council should establish an
ABC control rule based on scientific
advice from its SSC. The process of
establishing an ABC control rule could
also involve science advisors or the peer
review process established under
Magnuson-Stevens Act section
302(g)(1)(E). The ABC control rule
should clearly articulate how far below
the OFL, or OFL proxy, the ABC will be
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set based on the level of scientific
knowledge about the stock or stock
complex and the scientific uncertainty
in the estimate of OFL. The ABC control
rule should take into account
uncertainty in factors such as stock
assessment results, time lags in
updating assessments, the degree of
retrospective revision of assessment
results, and projections. The control
rule may be used in a tiered approach
to address different levels of scientific
uncertainty.
(5) Setting the annual catch limit—(i)
General. ACL cannot exceed the ABC
and may be set annually or on a
multiyear plan basis. A ‘‘multiyear
plan’’ as referenced in section 303(a)(15)
of the Magnuson-Stevens Act is a plan
that establishes harvest specifications or
harvest guidelines for each year of a
time period greater than 1 year. A
multiyear plan should include ACLs
and ACTs for each year with
appropriate AMs to prevent overfishing
and maintain an appropriate rate of
rebuilding if the stock or stock complex
is in a rebuilding plan. The AMs
specified for a multiyear plan should
provide that, if an ACL is exceeded for
a year, then a subsequent year’s harvest
specification (including ACLs and
ACTs) could be revised.
(ii) Sector ACLs. A Council may, but
is not required to, divide an ACL into
sector-ACLs. ‘‘Sector,’’ for purposes of
this section, means a distinct user group
to which separate management
strategies and separate catch quotas
apply. Examples of sectors include the
commercial sector, recreational sector,
or various gear groups within a fishery.
Sector-AMs must be developed for each
sector-ACL, and the sum of sector ACLs
must not exceed the stock or stock
complex level ACL. The system of ACLs
and AMs designed must be effective and
equitable and protect the stock or stock
complex as a whole. If sector-ACLs and
AMs are established, additional AMs at
the stock or stock complex level would
also be appropriate.
(iii) ACLs for State-Federal Fisheries.
For stocks or stock complexes that have
a large majority of harvest in state or
territorial waters, FMPs and FMP
amendments should include an ACL for
the overall stock that may be further
divided. For example, the overall ACL
could be divided into a federal-ACL and
state-ACL. However, NMFS recognizes
that federal management would be
limited to the portion of the fishery
under federal authority (see paragraph
(g)(5) of this section). When stocks are
co-managed by federal, state, tribal, and/
or territorial fishery managers, the goal
should be to develop collaborative
conservation and management
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strategies, and scientific capacity to
support such strategies, to prevent
overfishing of shared stocks and ensure
their sustainability.
(6) ACT control rule. For stocks and
stock complexes required to have an
ACL, each Council should establish
ACT control rules for setting the ACTs.
The ACT control rule should clearly
articulate how far below the ACL the
target will be established based on the
amount of management uncertainty
associated with harvest of a stock or
stock complex. For example, the ACT
may need to be set further below the
ACL in fisheries where inseason
monitoring of catch data is unavailable
or infeasible, or where AMs are
established using a multi-year averaging
approach (see paragraph (g)(4) of this
section).
(i) Determining management
uncertainty. Two sources of
management uncertainty should be
accounted for in establishing the ACT
control rule: Uncertainty in the ability
of managers to constrain catch to the
ACT and uncertainty in quantifying the
true catch amounts (i.e., estimation
errors). To determine the level of
management uncertainty in controlling
catch, analyses should consider past
management performance in the fishery
and factors such as time lags in reported
catch. Such analyses should be based on
the best available scientific information
from an SSC, agency scientists, or peer
review process as appropriate.
(ii) Establishing tiers and
corresponding ACT control rules. Tiers
can be established based on levels of
management uncertainty associated
with the fishery, frequency and
accuracy of catch monitoring data
available, and risks of exceeding the
limit. An ACT control rule could be
established for each tier and have, as
appropriate, different formulas and
standards used to establish the ACT.
(7) Relationships of OFL to MSY and
ACT to OY. The following (see
paragraphs (f)(7)(i) and (ii) of this
section) describes the relationships
between terms used in ending and
preventing overfishing and rebuilding
overfished stocks and stock complexes.
(i) Relationship of OFL to MSY. OFL
is the amount of catch for a particular
year that corresponds to the estimate of
MFMT applied to a stock or stock
complex’s abundance, and MSY is the
long-term average of such catches. ABC
is recommended to be set below OFL to
take into account the scientific
uncertainty in the estimate of OFL.
(ii) Relationship of ACT to OY.
Paragraphs (a) and (e)(3) of this section
define and describe OY and the goal of
preventing overfishing, while achieving
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on a continuing basis the OY from each
stock, stock complex, or fishery.
Management measures for a fishery
should, on an annual basis, achieve the
ACTs and prevent the ACLs from being
exceeded. The long-term objective is to
achieve OY through annual
achievement of ACT.
(g) Accountability measures. The
following features (see paragraphs (g)(1)
through (5) of this section) of
accountability measures apply to those
stocks and stock complexes in the
fishery.
(1) Introduction. AMs are
management controls that prevent ACLs
or sector-ACLs from being exceeded
(inseason AMs), where possible, and
correct or mitigate overages if they
occur. AMs should address and
minimize both the frequency and
magnitude of overages and correct the
problems that caused the overage in as
short a time as possible.
(2) Inseason AMs. Whenever possible,
FMPs should include inseason
monitoring and management measures
to prevent catch from exceeding ACLs.
Inseason AMs could include, but are not
limited to, closure of a fishery; closure
of specific areas; changes in gear;
changes in trip size or bag limits;
reductions in effort; or other appropriate
management controls for the fishery. If
final data or data components of catch
are delayed, Councils should make
appropriate use of preliminary data,
such as landed catch, in implementing
inseason AMs. Where timely catch data
are available for a stock, FMPs should
include inseason closure authority to
close the fishery on or before the date
when the ACL for a stock or stock
complex is projected to be reached.
(3) AMs for when the ACL is
exceeded. On an annual basis, the
Council should determine as soon as
possible after the fishing year if an ACL
was exceeded. If an ACL was exceeded,
AMs should be triggered and
implemented as soon as possible to
correct the operational issue that caused
the ACL overage, as well as any
biological consequences to the stock or
stock complex resulting from the
overage when it is known. These AMs
could include, among other things,
modifications of inseason AMs or
overage adjustments. For stocks and
stock complexes in rebuilding plans, the
AMs should include overage
adjustments that reduce the ACLs in the
next fishing year by the full amount of
the overages, unless the best scientific
information available shows that a
reduced overage adjustment, or no
adjustment is needed to mitigate the
effects of the overages. If catch exceeds
the ACL more than once in the last four
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years, the system of ACLs, ACTs and
AMs should be re-evaluated to improve
its performance and effectiveness.
(4) AMs based on multi-year average
data. Some fisheries have highly
variable annual catches and lack reliable
inseason or annual data on which to
base AMs. If there are insufficient data
upon which to compare catch to ACL,
either inseason or on an annual basis,
AMs could be based on comparisons of
average catch to average ACL over a
three-year moving average period or, if
supported by analysis, some other
appropriate multi-year period.
Evaluation of the moving average catch
to the average ACL must be conducted
annually. If the average catch exceeds
the average ACL more than once in the
last four years, then the ACL, ACT and
AM system should be re-evaluated. The
initial ACL and management measures
should incorporate information from
previous years so that AMs based on
average ACLs can be applied from the
first year.
(5) AMs for State-Federal Fisheries.
For stocks or stock complexes that have
a large majority of harvest in state or
territorial waters, AMs should be
developed for the portion of the fishery
under federal authority and could
include closing the EEZ when the
federal portion of the ACL is reached, or
the overall stock’s ACL is reached, or
other measures.
(h) Establishing ACL and AM
mechanisms in FMPs. FMPs or FMP
amendments should establish ACL and
AM mechanisms for all stocks and stock
complexes in the fishery, unless
paragraph (h)(2) of this section is
applicable. If a complex has multiple
indicator stocks, each indicator stock
must have its own ACL; an additional
ACL for the stock complex as a whole
is optional. In cases where fisheries
harvest multiple indicator stocks of a
single species that cannot be
distinguished at the time of capture,
separate ACLs for the indicator stocks
are not required and the ACL can be
established for the complex as a whole.
(1) In establishing ACL and AM
mechanisms, FMPs should describe:
(i) Timeframes for setting ACLs (e.g.,
annually or multi-year periods);
(ii) Sector-ACLs, if any (including setasides for research or bycatch);
(iii) AMs and their relationship to
ABC and ACT control rules, including
how AMs are triggered and what
sources of data will be used (e.g.,
inseason data, annual catch compared to
the ACL, or multi-year averaging
approach);
(iv) Sector-AMs, if there are sectorACLs; and
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(v) Fisheries data described in
paragraph (i) of this section.
(2) Exceptions from ACL and AM
requirements—(i) Life cycle. Section
303(a)(15) of the Magnuson-Stevens Act
‘‘shall not apply to a fishery for species
that has a life cycle of approximately 1
year unless the Secretary has
determined the fishery is subject to
overfishing of that species’ (as described
in Magnuson-Stevens Act section 303
note). This exception applies to a stock
for which the average length of time it
takes for an individual to produce a
reproductively active offspring is
approximately 1 year and that the
individual has only one breeding season
in its life time. While exempt from the
ACL and AM requirements, FMPs or
FMP amendments for these stocks
should have SDC, MSY, OY, ABC, and
an ABC control rule.
(ii) International fishery agreements.
Section 303(a)(15) of the MagnusonStevens Act applies ‘‘unless otherwise
provided for under an international
agreement in which the United States
participates’’ (Magnuson-Stevens Act
section 303 note). This exception
applies to stocks or stock complexes
subject to management under an
international agreement, which is
defined as ‘‘any bilateral or multilateral
treaty, convention, or agreement which
relates to fishing and to which the
United States is a party’’ (see MagnusonStevens Act section 3(24)). These stocks
would still need to have SDC and MSY.
(3) Flexibility in application of NS1
guidelines. There are limited
circumstances that may not fit the
standard approaches to specification of
reference points and management
measures set forth in these guidelines.
These include, among other things,
conservation and management of ESAlisted species, harvests from aquaculture
operations, and stocks with unusual life
history characteristics (e.g., Pacific
salmon, where the spawning potential
for a stock is spread over a multi-year
period). In these circumstances,
Councils may propose alternative
approaches for satisfying the NS1
requirements of the Magnuson-Stevens
Act than those set forth in these
guidelines. Councils should document
their rationale for any alternative
approaches for these limited
circumstances in an FMP or FMP
amendment, which will be reviewed for
consistency with the Magnuson-Stevens
Act.
(i) Fisheries data. In their FMPs,
Councils should describe general data
collection methods, as well as any
specific data collection methods used
for all stocks, stock complexes, and
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ecosystem component species. FMPs
should:
(1) List sources of fishing mortality
(both landed and discarded), including
commercial and recreational catch and
bycatch in other fisheries;
(2) Describe the data collection and
estimation methods used to quantify
total catch mortality in each fishery,
including information on the
management tools used (i.e., logbooks,
vessel monitoring systems, observer
programs, landings reports, fish tickets,
processor reports, dealer reports,
recreational angler surveys, or other
methods); the frequency with which
data are collected and updated; and the
scope of sampling coverage for each
fishery; and
(3) Describe the methods used to
compile catch data from various catch
data collection methods and how those
data are used to determine the
relationship between total catch at a
given point in time and the ACL for
stocks and stock complexes that are part
of a fishery.
(j) Council actions to address
overfishing and rebuilding for stocks
and stock complexes in the fishery—(1)
Notification. The Secretary will
immediately notify a Council whenever
it is determined that:
(i) Overfishing is occurring;
(ii) A stock or stock complex is
overfished;
(iii) A stock or stock complex is
approaching an overfished condition; or
(iv) Existing remedial action taken for
the purpose of ending previously
identified overfishing or rebuilding a
previously identified overfished stock or
stock complex has not resulted in
adequate progress.
(2) Timing of actions—(i) If a stock or
stock complex is undergoing
overfishing. FMPs or FMP amendments
should establish ACL and AM
mechanisms in 2010, for stocks and
stock complexes determined to be
subject to overfishing, and in 2011, for
all other stocks and stock complexes
(see paragraph (b)(2)(iii) of this section).
To address practical implementation
aspects of the FMP and FMP
amendment process, paragraphs
(j)(2)(i)(A) through (C) of this section
clarifies the expected timing of actions.
(A) In addition to establishing ACL
and AM mechanisms, the ACLs and
AMs themselves should be specified in
FMPs, FMP amendments, implementing
regulations, or annual specifications
beginning in 2010 or 2011, as
appropriate.
(B) For stocks and stock complexes
still determined to be subject to
overfishing at the end of 2008, ACL and
AM mechanisms and the ACLs and AMs
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32545
themselves should be effective in
fishing year 2010.
(C) For stocks and stock complexes
determined to be subject to overfishing
during 2009, ACL and AM mechanisms
and ACLs and AMs themselves should
be effective in fishing year 2010, if
possible, or in fishing year 2011, at the
latest.
(ii) If a stock or stock complex is
overfished or approaching an overfished
condition. (A) For notifications that a
stock or stock complex is overfished or
approaching an overfished condition
made before July 12, 2009, a Council
must prepare an FMP, FMP amendment,
or proposed regulations within one year
of notification. If the stock or stock
complex is overfished, the purpose of
the action is to specify a time period for
ending overfishing and rebuilding the
stock or stock complex that will be as
short as possible as described under
section 304(e) of the Magnuson-Stevens
Act. If the stock or stock complex is
approaching an overfished condition,
the purpose of the action is to prevent
the biomass from declining below the
MSST.
(B) For notifications that a stock or
stock complex is overfished made after
July 12, 2009, a Council must prepare an
FMP, FMP amendment, or proposed
regulations within two years of
notification. Council actions should be
submitted for Secretarial review within
15 months of notification to ensure
sufficient time for the Secretary to
implement the measures, if approved. If
the stock or stock complex is overfished
and overfishing is occurring, the
rebuilding plan must end overfishing
immediately and be consistent with
ACL and AM requirements of the
Magnsuon-Stevens Act.
(C) For notifications that a stock or
stock complex is approaching an
overfished condition made after July 12,
2009, a Council should take immediate
action to reduce the likelihood that the
stock or stock complex will become
overfished. Otherwise, the stock or stock
complex would likely be overfished by
the time the two-year timeline to
implement management measures
expired.
(3) Overfished fishery. (i) Where a
stock or stock complex is overfished, a
Council must specify a time period for
rebuilding the stock or stock complex
based on factors specified in MagnusonStevens Act section 304(e)(4). This
target time for rebuilding (Ttarget) shall
be as short as possible, taking into
account: The status and biology of any
overfished stock, the needs of fishing
communities, recommendations by
international organizations in which the
U.S. participates, and interaction of the
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stock within the marine ecosystem. In
addition, the time period shall not
exceed 10 years, except where biology
of the stock, other environmental
conditions, or management measures
under an international agreement to
which the U.S. participates dictate
otherwise. SSCs (or agency scientists or
peer review processes in the case of
Secretarial actions) shall provide
recommendations for achieving
rebuilding targets (see MagnusonStevens Act section 302(g)(1)(B)). The
above factors enter into the specification
of Ttarget as follows:
(A) The ‘‘minimum time for
rebuilding a stock’’ (Tmin) means the
amount of time the stock or stock
complex is expected to take to rebuild
to its MSY biomass level in the absence
of any fishing mortality. In this context,
the term ‘‘expected’’ means to have at
least a 50-percent probability of
attaining the Bmsy.
(B) For scenarios under paragraph
(j)(2)(ii)(A) of this section, the starting
year for the Tmin calculation is the first
year that a rebuilding plan is
implemented. For scenarios under
paragraph (j)(2)(ii)(B) of this section, the
starting year for the Tmin calculation is
2 years after notification that a stock or
stock complex is overfished or the first
year that a rebuilding plan is
implemented, whichever is sooner.
(C) If Tmin for the stock or stock
complex is 10 years or less, then the
maximum time allowable for rebuilding
(Tmax) that stock to its Bmsy is 10 years.
(D) If Tmin for the stock or stock
complex exceeds 10 years, then the
maximum time allowable for rebuilding
a stock or stock complex to its Bmsy is
Tmin plus the length of time associated
with one generation time for that stock
or stock complex. ‘‘Generation time’’ is
the average length of time between
when an individual is born and the
birth of its offspring.
(E) Ttarget shall not exceed Tmax,
should generally be less than Tmax, and
should be calculated based on the
factors described in this paragraph (j)(3)
with a priority given to rebuilding in as
short a time as possible.
(ii) If a stock or stock complex
reached the end of its rebuilding plan
period and has not yet been determined
to be rebuilt, then the rebuilding F
should not be increased until the stock
or stock complex has been demonstrated
to be rebuilt. If the rebuilding plan was
based on a Ttarget that was less than Tmax,
and the stock or stock complex is not
rebuilt by Ttarget, rebuilding measures
should be revised, if necessary, such
that the stock or stock complex will be
rebuilt by Tmax. If the stock or stock
complex has not rebuilt by Tmax, and the
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rebuilding F is greater than 75 percent
of MFMT, then the rebuilding F should
be reduced to no more than 75 percent
of MFMT until the stock or stock
complex has been demonstrated to be
rebuilt.
(iii) Council action addressing an
overfished fishery must allocate both
overfishing restrictions and recovery
benefits fairly and equitably among
sectors of the fishery.
(iv) For fisheries managed under an
international agreement, Council action
addressing an overfished fishery must
reflect traditional participation in the
fishery, relative to other nations, by
fishermen of the United States.
(4) Emergency actions and interim
measures. The Secretary, on his/her
own initiative or in response to a
Council request, may implement interim
measures to reduce overfishing or
promulgate regulations to address an
emergency (Magnuson-Stevens Act
section 304(e)(6) or 305(c)). In
considering a Council request for action,
the Secretary would consider, among
other things, the need for and urgency
of the action and public interest
considerations, such as benefits to the
stock or stock complex and impacts on
participants in the fishery.
(i) These measures may remain in
effect for not more than 180 days, but
may be extended for an additional 186
days if the public has had an
opportunity to comment on the
measures and, in the case of Councilrecommended measures, the Council is
actively preparing an FMP, FMP
amendment, or proposed regulations to
address the emergency or overfishing on
a permanent basis.
(ii) Often, these measures need to be
implemented without prior notice and
an opportunity for public comment, as
it would be impracticable to provide for
such processes given the need to act
quickly and also contrary to the public
interest to delay action. However,
emergency regulations and interim
measures that do not qualify for waivers
or exceptions under the Administrative
Procedure Act would need to follow
proposed notice and comment
rulemaking procedures.
(k) International overfishing. If the
Secretary determines that a fishery is
overfished or approaching a condition
of being overfished due to excessive
international fishing pressure, and for
which there are no management
measures (or no effective measures) to
end overfishing under an international
agreement to which the United States is
a party, then the Secretary and/or the
appropriate Council shall take certain
actions as provided under MagnusonStevens Act section 304(i). The
PO 00000
Frm 00061
Fmt 4702
Sfmt 4702
Secretary, in cooperation with the
Secretary of State, should immediately
take appropriate action at the
international level to end the
overfishing. In addition, within one year
after the determination, the Secretary
and/or appropriate Council shall:
(1) Develop recommendations for
domestic regulations to address the
relative impact of the U.S. fishing
vessels on the stock. Council
recommendations should be submitted
to the Secretary.
(2) Develop and submit
recommendations to the Secretary of
State, and to the Congress, for
international actions that will end
overfishing in the fishery and rebuild
the affected stocks, taking into account
the relative impact of vessels of other
nations and vessels of the United States
on the relevant stock. Councils should,
in consultation with the Secretary,
develop recommendations that take into
consideration relevant provisions of the
Magnuson-Stevens Act and NS1
guidelines, including section 304(e) of
the Magnuson-Stevens Act and
paragraph (j)(3)(iv) of this section, and
other applicable laws. For highly
migratory species in the Pacific,
recommendations from the Western
Pacific, North Pacific, or Pacific
Councils must be developed and
submitted consistent with MagnusonStevens Reauthorization Act section
503(f), as appropriate.
(3) Considerations for assessing
‘‘relative impact.’’ ‘‘Relative impact’’
under paragraphs (k)(1) and (2) of this
section may include consideration of
factors that include, but are not limited
to: Domestic and international
management measures already in place,
management history of a given nation,
estimates of a nation’s landings or catch
(including bycatch) in a given fishery,
and estimates of a nation’s mortality
contributions in a given fishery.
Information used to determine relative
impact should be based upon the best
available scientific information.
(l) Relationship of National Standard
1 to other national standards—(1)
National Standard 2 (see § 600.315).
Management measures and reference
points to implement NS1 must be based
on the best scientific information
available. When data are insufficient to
estimate reference points directly,
Councils should develop reasonable
proxies to the extent possible (also see
paragraph (e)(1)(iv) of this section). In
cases where scientific data are severely
limited, effort should also be directed to
identifying and gathering the needed
data. SSCs should advise their Councils
regarding the best scientific information
E:\FR\FM\09JNP1.SGM
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Federal Register / Vol. 73, No. 111 / Monday, June 9, 2008 / Proposed Rules
jlentini on PROD1PC65 with PROPOSALS
available for fishery management
decisions.
(2) National Standard 3 (see
§ 600.320). Reference points should
generally be specified in terms of the
level of stock aggregation for which the
best scientific information is available
(also see paragraph (e)(1)(iii) of this
section). Also, scientific assessments
should be based on the best information
about the total range of the stock and
potential biological structuring of the
stock into biological sub-units, which
may differ from the geographic units on
which management is feasible.
(3) National Standard 6 (see
§ 600.335). Councils must build into the
reference points and control rules
appropriate consideration of risk, taking
into account uncertainties in estimating
harvest, stock conditions, life history
parameters, or the effects of
environmental factors.
(4) National Standard 8 (see
§ 600.345). Councils must take into
account the importance of fishery
resources to fishing communities when
specifying OY and an ACT control rule.
Also, see paragraph (e)(3)(iv)(A) of this
VerDate Aug<31>2005
18:31 Jun 06, 2008
Jkt 214001
section for more information on how
factors that relate to fishing
communities should be considered
when reducing OY from MSY.
(5) National Standard 9 (see
§ 600.350). Evaluation of stock status
with respect to reference points must
take into account mortality caused by
bycatch. In addition, the estimation of
catch should include the mortality of
fish that are discarded.
(m) Exceptions to requirements to
prevent overfishing. Exceptions to the
requirement to prevent overfishing
could apply under certain limited
circumstances. Harvesting one stock at
its optimum level may result in
overfishing of another stock when the
two stocks tend to be caught together
(This can occur when the two stocks are
part of the same fishery or if one is
bycatch in the other’s fishery). Before a
Council may decide to allow this type
of overfishing, an analysis must be
performed and the analysis must
contain a justification in terms of overall
benefits, including a comparison of
benefits under alternative management
PO 00000
Frm 00062
Fmt 4702
Sfmt 4702
32547
measures, and an analysis of the risk of
any stock or stock complex falling
below its MSST. The Council may
decide to allow this type of overfishing
if the analysis demonstrates that all of
the following conditions are satisfied:
(1) Such action will result in longterm net benefits to the Nation;
(2) Mitigating measures have been
considered and it has been
demonstrated that a similar level of
long-term net benefits cannot be
achieved by modifying fleet behavior,
gear selection/configuration, or other
technical characteristic in a manner
such that no overfishing would occur;
and
(3) The resulting rate of fishing
mortality will not cause any stock or
stock complex to fall below its MSST
more than 50 percent of the time in the
long term, although it is recognized that
persistent overfishing is expected to
cause the affected stock to fall below its
Bmsy more than 50 percent of the time
in the long term.
[FR Doc. 08–1328 Filed 6–4–08; 9:34am]
BILLING CODE 3510–22–P
E:\FR\FM\09JNP1.SGM
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Agencies
[Federal Register Volume 73, Number 111 (Monday, June 9, 2008)]
[Proposed Rules]
[Pages 32526-32547]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 08-1328]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 600
[Docket No. 070717348-7766-02]
RIN 0648-AV60
Magnuson-Stevens Act Provisions; Annual Catch Limits; National
Standard Guidelines
AGENCY: National Marine Fisheries Service (NMFS); National Oceanic and
Atmospheric Administration (NOAA); Commerce.
ACTION: Proposed rule; request for comments.
-----------------------------------------------------------------------
SUMMARY: NMFS proposes revisions to the guidelines for National
Standard 1 (NS1) of the Magnuson-Stevens Fishery Conservation and
Management Act (MSA). This action is necessary to provide guidance on
how to comply with new annual catch limit (ACL) and accountability
measure (AM) requirements for ending overfishing of fisheries managed
by federal fishery management plans (FMPs). It also clarifies the
relationship between ACLs, maximum sustainable yield (MSY), optimum
yield (OY), and other applicable reference points. The intent of this
action is to facilitate compliance with requirements of the Magnuson-
Stevens Act to end and prevent overfishing, rebuild overfished stocks
and achieve OY.
DATES: Comments must be received by September 8, 2008.
ADDRESSES: You may submit comments, identified by 0648-AV60, by any of
the following methods:
Electronic Submissions: Submit all electronic public
comments via the Federal e-Rulemaking portal: https://
www.regulations.gov;
Fax: 301-713-1193, Attn: Mark Millikin;
Mail: Mark R. Millikin, National Marine Fisheries Service,
NOAA, Office of Sustainable Fisheries, 1315 East-West Highway, Room
13357, Silver Spring, MD 20910 (mark outside of envelope ``Comments on
Annual Catch Limits proposed rule'');
Instructions: All comments received are a part of the public record
and will generally be posted to https://www.regulations.gov without
change. All Personal Identifying Information (for example, name,
address, etc.) voluntarily submitted by the commenter may be publicly
accessible. Do not submit confidential business information or
otherwise sensitive or protected information.
NMFS will accept anonymous comments. Attachments to electronic
comments will be accepted in Microsoft Word, Excel, Wordperfect, or
Adobe PDF file formats only.
Copies of the Regulatory Impact Review (RIR)/Regulatory Flexibility
Act Analysis (RFAA) for this proposed rule are available from Mark R.
Millikin at the address listed above. The RIR/RFAA document is also
available via the internet at https://www.nmfs.noaa.gov/msa2007/
catchlimits.htm.
FOR FURTHER INFORMATION CONTACT: Mark R. Millikin, Senior Fishery
Management Specialist, 301-713-2341.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Overview of Proposed Revisions
II. Acronyms
III. Background
IV. NMFS's Proposed Rule for Further Revisions to NS1 Guidelines in
2005
V. NMFS's Initial Action on MSRA Requirements for ACLs
VI. MSRA Ending Overfishing Requirements
VII. Reasons for Overfishing and Expectations for ACLs to Prevent/
End Overfishing
[[Page 32527]]
VIII. Definition, Interpretation, and Application of the Term
``Fishery'' and Its Relevance to ACLs
A. Stocks in the Fishery
B. Ecosystem Component Species
C. Stocks Identified in More Than One FMP
D. Stock Complexes
IX. Statutory Exceptions to Requirements for ACLs and AMs and
Flexibility in Application of the NS1 Guidelines
X. MSRA Requirements for SSCs Related to ACLs
XI. MSY, OY, and SDC: A Review
XII. Description of the Relationship of OFL to MSY and ACT to OY
XIII. Definition Framework for OFL, ABC, ACL, and ACT
XIV. Control Rules
XV. Sector ACLs, ACTs, and AMs
XVI. Accountability Measures
XVII. Summary of Items to Include in FMPs
XVIII. Change in Timetable When Establishing a Rebuilding Plan
XIX. Establishing the Length of Time for a Rebuilding Plan
XX. Action When a Stock's Rebuilding Plan Ends and the Stock Is Not
Rebuilt
XXI. Changes to the definitions of Some Components of MSY
XXII. Social, Economic and Ecological Factors as They Relate to OY
XXIII. Scope of This Proposed Action
XXIV. Republishing Codified Text in Its Entirety
XXV. Classification
I. Overview of Proposed Revisions
NMFS fulfills the requirements of section 301(b) of the Magnuson-
Stevens Act--``The Secretary shall establish advisory guidelines (which
shall not have the force and effect of law), based on national
standards, to assist in the development of fishery management plans,''
with its national standard guidelines that appear at 50 CFR 600.310
through 50 CFR 600.355. NMFS is proposing revisions to the NS1
guidelines to address, among other things, new requirements for
fisheries undergoing overfishing, to have ACLs and AMs to end
overfishing by 2010, and all fisheries to have ACLs and AMs in place to
prevent or end overfishing by 2011, and beyond. A stock or stock
complex may not require an ACL and AMs if it qualifies for a statutory
exception under the Magnuson-Stevens Act. Other proposed revisions to
the NS1 guidelines include: (1) A description of the relationship
between MSY, OY, overfishing limits (OFL), acceptable biological catch
(ABC), ACLs, and annual catch targets (ACTs); (2) guidance on how to
combine the use of ACLs and AMs for a stock to prevent overfishing when
possible, and adjust ACTs or ACLs, or both, and AMs, if an ACL is
exceeded; (3) allowing for inclusion of ecosystem component (EC)
species in FMPs and, in such cases, guidance for how to classify which
stocks are ``in the fishery'' and which species are ecosystem
components; (4) replacing MSY control rules with ABC control rules and
replacing OY control rules with ACT control rules; (5) new requirements
for scientific and statistical committees (SSC); (6) changing the
timeline to prepare new rebuilding plans; (7) revised guidance on how
to establish rebuilding time targets; and (8) advice on action to take
at the end of a rebuilding period if a stock is not yet rebuilt.
II. Acronyms
ABC--acceptable biological catch
ACL--annual catch limit
ACT--annual catch target
AM--accountability measures
ANPR--Advance Notice of Proposed Rulemaking
Bmsy--MSY stock size
EC--ecosystem component species
EEZ--Exclusive Economic Zone
Fmsy--MSY fishing mortality rate
FMP--fishery management plan
MFMT--maximum fishing mortality threshold
MSA--Magnuson-Stevens Act
MSRA--Magnuson-Stevens Fishery Conservation and Management
Reauthorization Act
MSST--minimum stock size threshold
MSY--maximum sustainable yield
NOI--Notice of Intent
NS1--National Standard 1
OFL--overfishing limit
OY--optimum yield
SDC--status determination criteria
SFA--Sustainable Fisheries Act
SSC--scientific and statistical committee
Tmax--maximum time allowable for rebuilding a stock
Tmin--minimum time for rebuilding a stock
Ttarget--target time for rebuilding a stock
III. Background
The MSA serves as the chief authority for fisheries management in
the U.S. Exclusive Economic Zone (EEZ). Section 301(b) of the MSA
requires that ``The Secretary shall establish advisory guidelines
(which shall not have the force and effect of law), based on the
national standards, to assist in the development of fishery management
plans.'' Guidelines for the national standards are codified in subpart
D of 50 CFR part 600. The guidelines for national standards were last
revised through a final rule published in the Federal Register on May
1, 1998 (63 FR 24212), by adding revisions to the guidelines for
National Standards 1 (optimum yield), 2 (scientific information), 4
(allocations), 5 (efficiency), and 7 (costs and benefits); and adding
new guidelines for National Standards 8 (communities), 9 (bycatch), and
10 (safety of life at sea).
The guidelines for NS1 were revised extensively in the final rule
published on May 1, 1998, to bring them into conformance with revisions
to the MSA, as amended in 1996 by the Sustainable Fisheries Act (SFA).
In particular, the 1998 revisions to the NS1 guidelines addressed new
requirements for FMPs brought about by SFA amendments to MSA section
304(e) (rebuilding overfished fisheries).
The Magnuson-Stevens Fishery Conservation and Management
Reauthorization Act of 2006 (MSRA), which President Bush signed into
law on January 12, 2007, included new requirements regarding preventing
and ending overfishing and rebuilding fisheries. Therefore, NMFS is
proposing revisions to the NS1 guidelines at 50 CFR 600.310, to
integrate these new requirements with existing provisions related to
overfishing, rebuilding overfished stocks, and achieving optimum yield.
IV. NMFS's Proposed Rule for Further Revisions to NS1 Guidelines in
2005
NMFS published an advance notice of proposed rulemaking (ANPR) in
2003 (68 FR 7492, February 14, 2003), and a proposed rule in 2005 (70
FR 36240, June 22, 2005), in the Federal Register to propose further
revisions to the NS1 guidelines. NMFS sought to improve the utility of
the 1998 guidelines in assisting the regional fishery management
councils, and the Secretary of Commerce (Secretary) in the case of a
Secretarial Amendment or a Secretarial FMP (denoted collectively
hereafter as ``Councils,'' as 50 CFR 600.305(c)(11) provides that
``Council'' includes both the regional fishery management councils and
the Secretary when preparing FMPs or amendments), when establishing or
revising status determination criteria (SDC) for overfishing and
overfished definitions for stocks, and constructing or revising
rebuilding plans for overfished stocks.
Although NMFS received many public comments on the ANPR and the
2005 proposed rule, NMFS decided not to pursue publication of a final
rule when it learned that Congress was preparing an amendment to the
MSA that seemed likely to revise how to manage stocks undergoing
overfishing and stocks that need a rebuilding plan. Congress's efforts
culminated in passage of the 2006 MSRA.
[[Page 32528]]
V. NMFS's Initial Action on MSRA Requirements for ACLs
NMFS published a notice of intent (NOI) to prepare an environmental
impact statement (EIS) and commencement of a scoping period for ACLs
and AMs in the Federal Register on February 14, 2007 (72 FR 7016), with
a comment period ending date of April 17, 2007. NMFS held nine scoping
sessions, one associated with each of the eight Regional Fishery
Management Councils' meetings and one at NMFS Headquarters in Silver
Spring, MD. Comments that NMFS received are contained in ``Summary of
Comments Received on NMFS Proposal to Develop Guidance on ACLs and AMs,
July 2007,'' that is available at the NMFS Web site: https://
www.nmfs.noaa.gov/msa2007/catchlimits.htm.
The NOI indicated that an environmental assessment or EIS would be
prepared for this action. However, NMFS has decided that, for purposes
of compliance with the National Environmental Policy Act, a categorical
exclusion is appropriate for this action. The proposed action would
provide general guidance on ACL and AM and other requirements, but
there is considerable diversity in federally-managed fisheries and
FMPs. Thus, any analysis of the environmental, economic, and social
impacts of the NS1 guidelines would be highly speculative. Potential
environmental, economic, and social impacts cannot be meaningfully
analyzed until the Councils apply the guidelines to specific fisheries
and FMPs. At that time, the Councils would prepare an EIS or EA, as
appropriate.
VI. MSRA Ending Overfishing Requirements
Section 104(a)(10) of the MSRA established new requirements to end
and prevent overfishing, including ACLs and AMs. Section 303(a)(15) was
added to the MSA to read as follows: ``establish a mechanism for
specifying annual catch limits in the plan (including a multiyear
plan), implementing regulations, or annual specifications, at a level
such that overfishing does not occur in the fishery, including measures
to ensure accountability.'' ACLs and AMs are required by fishing year
2010 if overfishing is occurring in a fishery, and they are required
for all other fisheries by fishing year 2011.
In practical terms, given the time it takes to prepare and
implement an FMP amendment, if the status of one or more stocks in a
fishery at the end of 2008 is ``subject to overfishing,'' Councils
should submit ACL and AM mechanisms and actual ACLs for that fishery to
be effective in fishing year 2010. If overfishing is determined to be
occurring in a fishery in 2009, Councils should submit ACL and AM
mechanisms and actual ACLs for that fishery to be effective in fishing
year 2010, if possible, or in fishing year 2011, at the latest. All
fisheries must have ACL and AM mechanisms and actual ACLs by the
fishing year 2011, and beyond. The Secretary should amend Secretarial
FMPs, to comply with ACL and AM requirements on the same timetable.
Section 305(c) of the MSA, which was unchanged by MSRA, also provides
authority to the Secretary to promulgate emergency regulations or
interim measures necessary to address an emergency or overfishing for
any fishery without regard to whether an FMP exists for such fishery.
NMFS recognizes that the phrase, ``at a level such that overfishing
does not occur'' in section 303(a)(15) of the MSA is subject to
different interpretations, as reflected in the varying comments
received during scoping. On the one hand, the phrase could be
interpreted to mean that overfishing is strictly prohibited at any
cost. On the other hand, section 303(a)(15) refers to a ``mechanism''
for setting ACLs, including AMs, which seems to imply a more dynamic
process that allows for adjustment of management measures as a fishery
is carried out. The only way to ensure absolutely no overfishing occurs
is to stop fishing. As long as fishing occurs, there is a chance for
occasional instances of overfishing due to scientific uncertainty of
data, influence of non-fishing factors, and management uncertainty.
Continued overfishing for a period of years (chronic overfishing),
presents the greatest danger to the health of fish stocks, and often
leads to stocks becoming overfished. NMFS has noted that overfished
stocks with chronic overfishing seem to seldom rebuild, whereas
overfished stocks that are rarely subject to overfishing have a better
chance of rebuilding.
Taking the above considerations into account, NMFS believes that
the ACL requirement should be interpreted to provide for some
flexibility given scientific and management uncertainty and other
factors, but at the same time, must address overfishing and facilitate
rebuilding. Chronic overfishing can be prevented by ensuring that the
combination of ACLs and AMs decrease the risk of future overfishing
each successive time an ACL is exceeded. NMFS thus proposes a
performance standard such that if catch of a stock exceeds its ACL more
often than once in the last four years (i.e., more often than 25
percent of the time), then the system of ACLs, ACTs and AMs should be
re-evaluated to improve its performance and effectiveness (see Sec.
600.310(g)(3) in this proposed action). NMFS believes that allowing a
higher frequency of the ACL being exceeded would not safeguard enough
against overfishing. A Council could choose a higher performance
standard (e.g., a stock's catch should not exceed its ACL more often
than once every five or six years) for a stock that is particularly
vulnerable to the effects of overfishing.
VII. Reasons for Overfishing and Expectations for ACLs to Prevent/End
Overfishing
The ``NMFS Fourth Quarterly Report for 2007 Status of U.S.
Fisheries'' indicates that 41 stocks managed by federal FMPs were
undergoing overfishing as of December 31, 2007. Stocks become listed as
``overfishing'' or remain in an overfishing status for a variety of
reasons, including:
1. The goal of the FMP may be to end overfishing over several years
by gradually reducing fishing mortality rates instead of ending
overfishing immediately.
2. Management measures have proven ineffective at ending
overfishing (e.g., lack of inseason closure authority for the fishery
or management measures are aimed at achieving a target catch that is
set too close to the catch amount that results in overfishing, or
both).
3. Management measures to address overfishing have not been
implemented yet.
4. Recent change in scientific advice (i.e., the Council has not
had sufficient time to amend the FMP and no automatic measures exist in
the FMP to make necessary adjustments to end overfishing in the
subsequent fishing year).
5. Bycatch mortality in other fisheries has not been addressed
adequately or is poorly known.
6. Data sufficient to verify whether or not overfishing is
occurring are not available, so the existing overfishing determination
is retained.
7. International fishing pressure is responsible for the large
majority of overfishing.
8. Fishing pressure in state or territorial waters is responsible
for the large majority of overfishing, federal action alone is not
sufficient to end overfishing, and managers in the various
jurisdictions are unable thus far to agree on a concerted approach for
preventing overfishing.
NMFS believes that the ACL and AM requirements will address
overfishing that results from reasons 1, 2, 3, and 4
[[Page 32529]]
above. Better scientific data, along with adequate ACLs and AMs, should
enable Councils to prevent overfishing for reasons 5 and 6. Stocks that
are undergoing overfishing for reason 7 would be exempt from the ACL
requirement (see Sec. Sec. 600.310(h)(2)(ii) and 600.310(k) of this
proposed action for discussion of international fisheries). There may
be circumstances where managers in various jurisdictions are unable to
agree on an ACL and AMs that would end or prevent overfishing for a
fishery described under reason 8. In such cases, these proposed
guidelines would require an ACL for the overall fishery, but AMs would
be implemented only for the portion of the fishery under federal
management authority.
VIII. Definition, Interpretation, and Application of the Term
``Fishery'' and Its Relevance to ACLs
The MSA, as amended by MSRA, requires that a Council shall develop
ACLs ``for each of its managed fisheries'' (see MSA section 302(h)(6))
and as noted earlier, that each FMP have a mechanism for specifying
ACLs ``at a level such that overfishing does not occur in the fishery''
(see MSA section 303(a)(15)). Consistent with these sections of the
MSA, the proposed NS1 guidelines provide that ACLs and AMs are needed
for each ``fishery'' under federal FMP management, unless covered by a
statutory exception.
The MSA defines ``fishery'' broadly, and this definition did not
change with the passage of the MSRA. A ``fishery'' is ``one or more
stocks of fish which can be treated as a unit for purposes of
conservation and management and which are identified on the basis of
geographical, scientific, technical, recreational and economic
characteristics,'' and ``any fishing of such stocks'' (see MSA section
3(13) and 50 CFR 600.10). The term ``fishery'' can mean different
things in different contexts. For example, when dealing with biological
concepts such as determining a status of overfishing or overfished, the
NS1 guidelines generally apply at the ``stock or stock complex'' level
(See, e.g., 50 CFR 600.310(c)(1), (d) (defining MSY and ``overfish''
with regard to ``stock or stock complex'') and Sec. 600.305(c)(12)
(explaining that ``stock or stock complex'' is used as a synonym for
``fishery'' in NS guidelines). In other instances, such as managing a
fishery for OY, the term ``fishery'' is viewed more broadly (see 50 CFR
600.310(f) (referring to OY at the ``fishery'' and not the ``stock or
stock complex'' level)).
Given the broad definition of ``fishery,'' the Councils have had,
and continue to have, considerable discretion in defining the
``fishery'' under FMPs. Some FMPs include only one or a few stocks
whereas others include several or hundreds of species. Looking at
existing FMPs, the primary reasons why stocks are included in FMPs are
because people seek to harvest them for sale or personal use (i.e., the
fish are the target of fishing activity), or they are caught
incidentally in the pursuit of harvesting one or more other stocks and
could experience overfishing or become overfished without conservation
and management measures. These reasons are consistent with the stated
purposes of the MSA, which includes the preparation and implementation
of FMPs ``which will achieve and maintain, on a continuing basis, the
optimum yield from each fishery'' (see MSA section 2(b)(4)). OY is
defined with regard to ``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'' (see MSA section 3(33)).
While the focus of FMPs has been stocks managed for OY, in recent
years, some FMPs have included other stocks in an effort to incorporate
ecosystem approaches to management. Congress acknowledged this
increased attention to ecosystem approaches in the ``Findings'' section
of the Act (see MSA section 2(a)(11) (acknowledging that a number of
Councils have demonstrated significant progress in integrating
ecosystem considerations under existing authorities of the MSA)). In
addition, MSRA added a new section 303(b)(12) that provides that an FMP
may ``include management measures in the plan to conserve target and
non-target species and habitats, considering the variety of ecological
factors affecting fishery populations.''
NMFS wants to encourage ecosystem approaches to fishery management
and believes that clarification of what constitutes the ``fishery''
would be helpful. As such, NMFS is proposing guidance pertaining to
``stocks in the fishery'' and ``ecosystem component (EC) species,''
which are described in detail below. The intent of this guidance is to
articulate approaches taken under existing FMPs and to provide a
framework for thinking about future FMPs and FMP amendments. The
Councils would have the discretion to determine, on a case-by-case
basis, whether changes in their stock classifications under current
FMPs are needed.
A. Stocks in the Fishery
As a default, all stocks currently identified in an FMP are
considered ``stocks in the fishery.'' ``Stocks in the fishery'' would
include target stocks (i.e., stocks that fishers seek to catch for sale
or personal use, including ``economic discards'' as defined under MSA
section 3(9)), non-target stocks that are retained for sale or personal
use, and non-target stocks that are not retained for sale or personal
use and that are either determined to be subject to overfishing,
approaching overfished, or overfished, or could become so, according to
the best scientific information available, without conservation and
management measures (see Figure 1 and Sec. 600.310(d)(2) of this
proposed action). Stocks and stock complexes in the fishery should have
quantitative SDC, MSY, ABC, ACL, and ACT (collectively called
``reference points'' throughout this section) and AMs (see Table 1 for
reference points needed for different types of stocks, and see Sec.
600.310(b)(2)(iv) of this proposed action), although some stocks in the
fishery may not require ACLs and AMs if they are covered by a statutory
exception (see Sec. 600.310(h)(2) of this proposed action). Hereafter,
in these guidelines, ``stock'' or ``stock(s) and stock complex(es)''
refer to ``stocks in the fishery.''
B. Ecosystem Component Species
Beyond the ``stocks in the fishery,'' a Council may, but is not
required to, include EC species in an FMP. Such species would include
non-target fish species that are not considered part of the ``fishery''
but rather species with which the fishery may occasionally interact
(i.e., catch) (see Sec. 600.310(d)(5) of this proposed action). A
Council may choose to include EC species for purposes of incorporating
ecosystem approaches to fishery management, data collection, etc.
Identification of EC species must be done through an FMP amendment
process (see Sec. 600.310(d) of this proposed action). Such species
are appropriate to consider when addressing specification of OY and
conservation and management measures for the fishery (see MSA sections
3(33) (referring to taking into account the marine ecosystems in OY
definition), and 3(5) (referring to avoiding irreversible or long-term
effects on fishery resources and the marine environment and ensuring
multiplicity of options)). Because EC species are not considered to be
``in the fishery,'' specification of reference points, ACLs, and AMs
are not required (see Table 1). However, a Council should consider
[[Page 32530]]
measures for the fishery to minimize bycatch and bycatch mortality of
EC species consistent with National Standard 9, and to protect their
associated role in the ecosystem. NMFS is especially interested in the
public's comments on the appropriate criteria for classification of EC
species.
C. Stocks Identified in More Than One FMP
If a stock is identified as part of more than one ``fishery,''
Councils should choose which FMP will be the ``primary FMP'' in which
management objectives, SDC, and other reference points for the stock
are established. In most cases, the primary FMP for a stock will be the
one in which the stock is identified as a target stock. Other FMPs in
which the stock is identified as part of a fishery should contain
management measures consistent with the primary FMP for the stock.
[GRAPHIC] [TIFF OMITTED] TP09JN08.000
Table 1.--Reference Points, Accountability Measures, and Control Rules That Would Be Required or Recommended
----------------------------------------------------------------------------------------------------------------
Stocks and stock
complexes in a Stocks and stock
fishery (excluding Stocks and stock complexes in a
those with an complexes in a fishery managed Ecosystem
Reference points, accountability approximate 1 year fishery that have a under an component
measures, and control rules life cycle and those life cycle of international species \4\
managed under approximately 1 year fishery agreement
international \3\
fishery agreements)
----------------------------------------------------------------------------------------------------------------
MSY \1\.......................... [check]............. [check]............. [check]............. N/A
SDC \1\ (e.g. MFMT \2\, MSST \2\) [check]............. [check]............. [check]............. N/A
OY \1\........................... At the stock, stock At the stock, stock R................... N/A
complex, or fishery complex, or fishery
level. level.
OFL \2\.......................... R................... R................... R................... N/A
ABC \1\.......................... [check]............. [check]............. R................... N/A
ACL \1\.......................... [check]............. Only if ``subject to R................... N/A
overfishing''.
AMs \1\.......................... [check]............. Only if ``subject to R................... N/A
overfishing''.
ACT \2\.......................... [check]............. Only if ``subject to R................... N/A
overfishing''.
ABC control rule \2\............. [check]............. [check]............. R................... N/A
ACT control rule \2\............. [check]............. R................... R................... N/A
----------------------------------------------------------------------------------------------------------------
\1\ MSA requirement.
\2\ For consistency with the NS1 Guidelines.
\3\ If the stock is in a U.S. FMP and managed under an international fishery agreement to which the U.S. is
party.
\4\ Not required by MSA, but an option provided in the NS1 Guidelines.
Legend:
[check] = Yes, this is applicable.
ABC = Acceptable Biological Catch.
ACL = Annual Catch Limit.
AM = Accountability Measures.
MFMT = Maximum Fishing Mortality Threshold.
MSST = Minimum Stock Size Threshold.
[[Page 32531]]
MSY = Maximum Sustainable Yield.
N/A = Not Applicable.
OFL = Overfishing Limit.
OY = Optimum Yield.
R = Recommended.
SDC = Status Determination Criteria.
D. Stock Complexes
``Stock complex'' means a group of stocks in an FMP that are
sufficiently similar in geographic distribution, life history, and
vulnerability to the fishery that the impacts of management actions on
the stocks in the complex is similar (see Sec. 600.310(d)(8) of this
proposed action). Stock complexes may be comprised of: (1) One or more
indicator stocks, each of which has SDC and ACLs, and several other
stocks; (2) several stocks without an indicator stock, with SDC and an
ACL for the complex as a whole; or (3) one or more indicator stocks,
each of which has SDC and management objectives, with an ACL for the
complex as a whole (this situation might be applicable to some salmon
species).
For stock complexes, the SDC measured on a stock complex-wide basis
or for an indicator stock should satisfy the MSA's requirements to
prevent overfishing and achieve OY for a fishery. Vulnerability of
stocks to the fishery should be evaluated when determining if: (1) A
particular stock complex should be established or reorganized; (2) a
particular stock should be a member of a stock complex; or (3) a stock
complex should be reorganized. Indicator stocks are stocks selected as
a representative for a stock complex because they have known
determinations regarding SDC, and known values for MSY and OY, and can
form the basis for an MSY and OY for the combinations of stocks in a
complex. Although it is common for the indicator stock for a stock
complex to be the most abundant stock, if an indicator stock is less
vulnerable than other stocks in the complex, the management measures
should be more conservative to protect the more vulnerable stocks from
overfishing.
IX. Statutory Exceptions to Requirements for ACLs and AMs and
Flexibility in Application of NS1 Guidelines
The MSRA provides two statutory exceptions to the ACL and AM
requirements under MSA section 303(a)(15) (see MSRA section 104(b)
(adding two exceptions under a MSA section 303 note); see also Sec.
600.310(h)(2) of this proposed action). First, MSA section 303(a)(15)
``shall not apply to a fishery for species that have a life cycle of
approximately 1 year unless the Secretary has determined the fishery is
subject to overfishing of that species'' (see MSRA section 104(b)(2)).
NMFS interprets ``fishery for species'' to be a stock. In addition,
NMFS interprets ``a life cycle of approximately 1 year'' to mean that
the average length of time it takes for an individual to produce a
reproductively active offspring is approximately 1 year, and that the
individual has only one breeding season in its lifetime. While stocks
that qualify for the 1-year life cycle exception would not need to have
ACLs and AMs, such stocks should still have SDC, MSY, OY, ABC, and an
ABC control rule.
Second, MSA section 303(a)(15) shall take effect in 2010 and 2011,
as discussed earlier, ``unless otherwise provided for under an
international agreement in which the United States participates'' (see
MSRA section 104(b)(1)). It is not clear to what the text ``unless
otherwise provided for'' is referring. NMFS has considered several
possible interpretations of this text in light of other provisions in
MSRA, including the new international overfishing provisions in MSA
section 304(i). Prior to MSRA, fisheries managed under international
agreements in which the United States participates (referred to in this
action as ``international fisheries'') were subject to MSA section
304(e) requirements regarding overfishing and rebuilding. However, in
many of these fisheries, the United States could not unilaterally end
overfishing or rebuild the stocks. New MSA section 304(i) and other
MSRA provisions acknowledge the increasing problem of international
overfishing and the challenges of establishing conservation and
management measures at the international level. Given Congress's
recognition of the increasing problem of international overfishing and
the complexities of international negotiation, NMFS believes that the
ACL exception should apply to fisheries that are subject to management
under international agreements in which the United States participates.
Applying ACLs or AMs only to the U.S. portion of the catch would not
effect rebuilding or end overfishing, would potentially disadvantage
U.S. fishermen with respect to foreign fishermen, and could weaken U.S.
negotiating positions at international fora in which it participates.
Apart from the statutory exceptions, NMFS recognizes that there are
limited circumstances that do not fit the standard approaches to
specification of reference points and management measures set forth in
the proposed revisions to the NS1 guidelines. These include, among
other things, conservation and management of ESA-listed species,
harvests from aquaculture operations, and stocks with unusual life
history characteristics (e.g., Pacific salmon, where the spawning
potential for a stock is spread over a multi-year period). For
fisheries where ESA-listed species are incidentally caught, the ESA
recovery plan would be a significant driver for setting management
objectives, including ACLs, for the fishery. For aquaculture, once
managers address status of broodstock taken from the wild (i.e.,
whether overfishing is occurring and/or whether the stock is in need of
rebuilding), then the levels of harvests from an aquaculture facility
would not necessarily need to focus on ending or preventing overfishing
or rebuilding stocks. In these circumstances, Councils may propose
alternative approaches for satisfying the NS1 requirements of the
Magnuson-Stevens Act other than those set forth in these guidelines.
Councils should document their rationale for any alternative approaches
for these limited circumstances in an FMP or FMP amendment, which will
be reviewed for consistency with the Magnuson-Stevens Act.
For a fishery in a federal FMP that has a large majority of harvest
in state or territorial waters, the fishery should have ACL that takes
into account the overall status of the stock, whether in state or
federal waters or beyond. However, NMFS recognizes that AMs could only
be applied to the portion of the fishery under federal jurisdiction.
Given the jurisdictional issue, one approach proposed is that the
overall ACL could be divided into a federal portion (federal-ACL) and a
state portion (state-ACL). AMs would then be triggered when the
federal-ACL was reached or projected to be reached (see further
explanation in ``Accountability Measures'' section below).
X. MSRA Requirements for SSCs Related to ACLs
The MSRA added new requirements for SSCs in the MSA. New section
[[Page 32532]]
302(g)(1)(B) of the MSA states that an SSC for each Regional Fishery
Management Council ``shall provide its Council ongoing scientific
advice for fishery management decisions, including recommendations for
acceptable biological catch, preventing overfishing, maximum
sustainable yield, and achieving rebuilding targets, and reports on
stock status and health, bycatch, habitat status, social and economic
impacts of management measures, and sustainability of fishing
practices.'' New section 302(g)(1)(E) provides that ``The Secretary and
each Council may establish a peer review process for that Council for
scientific information used to advise the Council about the
conservation and management of the fishery.'' In addition, new section
302(h)(6) provides that each Regional Fishery Management Council is
required to ``develop annual catch limits for each of its managed
fisheries that may not exceed the fishing level recommendations of its
scientific and statistical committee or the peer review process
established under subsection (g).''
NMFS recognizes that there is variability in the peer review
processes and involvement of SSCs amongst the various Councils. In
addition, the above statutory sections could be subject to different
interpretations. While MSA section 302(h)(6) refers generally to
``fishing level recommendations,'' section 302(g)(1)(B) refers to
recommendations for ABC and MSY, among other things, and section
302(g)(1)(E) refers generally to ``scientific information.'' Further,
the text provides for advice from the SSC but also refers to peer
review processes, leaving open a question about the role and
relationship between the two. NMFS believes that clear processes for
implementing these provisions are important in order to ensure that
Councils get the information needed to establish ACL mechanisms,
prevent confusion in the decision making process, and ensure general
consistency in approaches taken.
For purposes of setting ACLs, a critical piece of scientific advice
that Councils will need will be the ABC. Taking this into account, and
considering the new requirements in light of existing SSC, Council, and
peer review processes, NMFS proposes that the Councils establish a
process that could be included in their Statement of Organization,
Practices and Procedures (see Sec. 600.115) which will: Establish an
ABC control rule, identify the body that will apply the ABC control
rule (i.e., calculates the ABC), identify the review process that will
verify the resulting ABC, and confirm that the SSC recommends the ABC
to the Council. For Secretarial FMPs or FMP amendments, agency
scientists or a peer review process would provide the scientific advice
to establish ABC. For fisheries managed under international agreements
in which the United States participates (referred to in this action as
``international fisheries''), stock assessments are conducted through
international scientific bodies that may include U.S. and non-U.S.
scientists. While the United States promotes fishery conservation and
management principles as embodied in the MSA (see, e.g., MSA section
102(c)), it cannot guarantee that international actions will be
consistent with the Act or NS1 guidelines. Thus, an ABC as defined in
these guidelines would not be required for international fisheries.
For stock and stock complexes required to have an ABC, NMFS
recommends that each Council should establish an ABC control rule (see
Sec. 600.310(f)(4) of this proposed action) based on scientific advice
from its SSC. The process of establishing an ABC control rule could
also involve science advisors or the peer review process established
under MSA section 302(g)(1)(E). Stock assessment scientists, a plan
development team, or other designated body would then apply the ABC
control rule. If a peer review process is established it should
investigate the technical merits of stock assessments and other
scientific information used by the SSC. For example, a peer review
process (e.g., Stock Assessment Review Panel) could validate the ABC
calculation and then pass their results to the SSC. Ultimately, the SSC
should make the formal ABC recommendation to the Council. For Council-
managed fisheries, the peer review process is not a substitute for the
SSC, and should work in conjunction with the SSC.
XI. MSY, OY, and SDC: A Review
MSY, OY, and SDC are concepts described in the current NS1
guidelines, and MSRA did not effect changes to the MSA that would
require changes to these concepts. The following sections provide a
review of MSY, OY, and SDC and an explanation of the relationship
between them and the proposed guidance on ACLs and other requirements.
MSY is the largest long-term average catch or yield that can be
taken from a stock or stock complex under prevailing ecological and
environmental conditions and fishery technological characteristics. Any
estimate of MSY depends on the population dynamics of the stock and the
characteristics of the fisheries (e.g. gear selectivity). MSY stock
size (Bmsy) is the long-term average size of the stock or stock
complex, measured in terms of spawning biomass, or other appropriate
measure of the stock's reproductive potential, that would be achieved
by fishing at Fmsy. OY is the amount of fish that will provide the
greatest overall benefit to the Nation, while preventing overfishing,
particularly with respect to food production and recreational
opportunities, and taking into account the protection of marine
ecosystems. OY is prescribed on the basis of the MSY from the fishery,
as reduced by relevant economic, social or ecological factors. In the
case of an overfished fishery, OY provides for rebuilding to a level
consistent with producing MSY in such a fishery. In NS1, use of the
phrase, ``achieving, on a continuing basis, the optimum yield from each
fishery'' means producing, from each stock, stock complex or fishery a
long-term series of catches such that the average catch is equal to OY,
overfishing is prevented, the long term average biomass is near or
above Bmsy, and overfished stocks are rebuilt in as short a time as
possible as specified in MSA section 304(e)(4). OY might be established
at the stock or stock complex level, or for a fishery comprised of
stocks, many of which have their own ACL and ACT (e.g., groundfish of
the Gulf of Alaska and groundfish of the Bering Sea and Aleutian
Islands).
Section 3(34) of the MSA states that ``overfishing'' and
``overfished'' mean a rate or level of fishing mortality that
jeopardizes the capacity of a fishery to produce the maximum
sustainable yield on a continuing basis. To reduce confusion and
conform to usage of those terms in other fisheries worldwide, in the
current NS1 guidelines, NMFS interpreted these terms so that
``overfished'' pertains to the biomass of the stock or stock complex,
and ``overfishing'' pertains to a rate or level of removal of fish from
the stock or stock complex. The current NS1 guidelines also provide for
SDC, which are quantifiable factors for determining whether a stock or
stock complex is overfished or if overfishing is occurring. An
overfished definition consists of a measure of stock abundance called
the minimum stock size threshold (MSST), below which a stock's or stock
complex's capacity to produce MSY on a continuing basis is jeopardized.
Overfishing of a stock or stock complex occurs whenever a stock or
stock complex is subjected to a rate or level of fishing mortality,
called the
[[Page 32533]]
maximum fishing mortality threshold (MFMT), above which the stock's or
stock complex's capacity to produce MSY on a continuing basis is
jeopardized or annual catch exceeds a stock's or stock complex's OFL.
MSRA made no changes to the MSA that would necessitate different
interpretations of these terms or different approaches to these
concepts.
XII. Description of the Relationship of OFL to MSY and ACT to OY
National Standard 1 establishes the relationship between
conservation and management measures, preventing overfishing, and
achieving OY from each stock, stock complex or fishery. The following
sections describe in detail NMFS' proposed guidance on ACLs and other
new requirements. Among other things, the proposed guidance introduces
new terms--overfishing limit (OFL) and annual catch target (ACT)--which
are not set forth in the MSA but which NMFS believes would be helpful
to implement the statutory requirements. As an overview, OFL is an
annual amount of catch that corresponds to the estimate of MFMT applied
to a stock or complex's abundance; MSY is the long-term average of such
catches. The current NS1 guidelines define overfishing with regard to
MFMT, which is a rate of fishing. The use of OFL would provide another
method for measuring overfishing by allowing the comparison of a stock
or stock complexes' annual catch to its OFL; if catch exceeds OFL,
overfishing is occurring. It is recommended that ABC would be set below
OFL to take into account the scientific uncertainty in the estimate of
OFL.
ACL would be the limit that triggers AMs, and ACT would be the
management target for the fishery. Management measures for a fishery
should, on an annual basis, achieve the ACT and prevent the ACL from
being exceeded. The long-term objective is to achieve OY through annual
achievement of ACT.
XIII. Definition Framework for OFL, ABC, ACL, and ACT
The MSRA does not define ACLs, AMs, and ABC, and there are many
different ways in which these terms can be defined. The voluminous
comments that NMFS received during scoping reflects the wide range of
possible interpretations and approaches. For example, some commenters
felt that ACL should be considered a target catch level and others felt
it should be a limit that should not be approached or reached. Many
commenters suggested, in general, that a buffer be implemented between
management targets and limits in order to prevent overfishing and
account for uncertainty. Over the past year, NMFS spent considerable
time reviewing different interpretations of the ACL requirement in
light of MSA sections 303(a)(15), 302(h)(6), and 302(g) and other
sections of the MSA, and taking into consideration the current NS1
guidelines, previously proposed changes to those guidelines, existing
FMPs and FMP amendments, scientific and management roles in the
decision making process, and public comment. Based on this review, NMFS
proposes the following definitions for ACL, AM, and ABC, and also for
ACT and OFL:
1. Overfishing limit (OFL) means ``the annual amount of catch that
corresponds to the estimate of MFMT applied to a stock or stock
complex's abundance and is expressed in terms of numbers or weight of
fish.'' See Sec. 600.310(e)(2)(i)(D) of this proposed action.
2. Acceptable biological catch (ABC) means ``a level of a stock or
stock complex's annual catch that accounts for the scientific
uncertainty in the estimate of OFL and should be specified based on the
ABC control rule.'' See Sec. 600.310 (f)(2)(ii) of this proposed
action.
3. Annual catch limit (ACL) means ``the level of annual catch of a
stock or stock complex that serves as the basis for invoking
accountability measures.'' See Sec. 600.310(f)(2)(iv) of this proposed
action.
4. Annual catch target (ACT) means ``an amount of annual catch of a
stock or stock complex that is the management target of the fishery. A
stock or stock complex's ACT should usually be less than its ACL and
results from the application of the ACT control rule. If sector-ACLs
have been established, each one should have a corresponding sector-
ACT.'' See Sec. Sec. 600.310(f)(2)(v) and (f)(6) of this proposed
action.
5. Accountability measures (AMs) means ``management controls that
prevent ACLs or sector-ACLs from being exceeded (inseason AMs), where
possible, and correct or mitigate overages if they occur.'' See Sec.
600.310(g) of this proposed action.
As proposed in this action, the relationship between the above
terms would be OFL>=ABC>=ACL>=ACT (see Figure 2). Because a primary
goal of the MSA, and management responsibility of NMFS and the
Councils, is to end and prevent overfishing, rather than account for it
after it occurs, NMFS believes that a good approach to management is to
have OFL>ABC and ACL>ACT. The ABC is lower than the OFL to address
scientific uncertainty in the estimate of OFL, and ACT is lower than
the ACL to address uncertainty in the accounting for catch and in the
degree to which management measures can control catch to the target
level.
OFL is an annual amount of catch that corresponds to the estimate
of MFMT applied to a stock or complex's abundance, and MSY is the long-
term average of such catches. NMFS proposes that OFL be the upper bound
of ABC, but that ABC should usually be reduced from the OFL to account
for scientific uncertainty in the estimate of OFL. For overfished
stocks, ABC must also be set to reflect the annual catch that is
consistent with the rebuilding plan for that stock. Therefore, if a
stock is being managed under a rebuilding program, its ABC should be
lower during some or all stages of rebuilding than when the stock is
rebuilt. The ABC will be set on the basis of the ABC control rule.
The proposed guidelines would have the Councils set the ACL as a
level of catch specified for a stock or stock complex each year that
cannot exceed its ABC. If a stock or stock complex's catch exceeds its
ACL, AMs will be invoked as specified in the FMP. The ACL may typically
be equal to the ABC and setting the ACL provides an opportunity to
divide the total ACL into sector-specific ACLs. As noted above, the
purpose of the ACT is to address management uncertainty. The ACT would
be the target catch of a stock or stock complex that a fishery is
managed to attain and should generally be less than the stock or stock
complex's ACL. ``Catch'' includes fish that are retained for any
purpose, as well as mortality of fish that are discarded (see Sec.
600.310(f)(2)(i) of this proposed action). Therefore, for fisheries
where bycatch estimates are not available in a timely enough manner to
manage annual catch, targets may be specified for landings, so long as
an estimate of bycatch is accounted for such that total of landings and
bycatch will not exceed the stock's or stock complex's ACL. For a stock
with sufficient inseason data monitoring, the fishery for that stock
would be closed in time to prevent the ACL from being exceeded.
NMFS notes that when it published an initial notice about ACLs, ACT
was not a parameter used when exploring the concept of how to make ACLs
and AMs operational. At that time, NMFS suggested an initial approach
of OFL>ABC>=ACL with ACL as the target catch that management measures
should try to attain. Under that approach, if catch of a stock reached
the OFL, its
[[Page 32534]]
fishery would be closed. During the scoping period, NMFS received some
public comments expressing concern about the use of an ACL as a
management target as opposed to a ``limit.'' Also, the framework
contained in this proposed rule provides for better separation between
scientific uncertainty in estimating OFL (i.e., a recommendation that
ABC be lower than OFL), and management uncertainty and OY factors
indicating that an ACT be lower than the ACL.
[GRAPHIC] [TIFF OMITTED] TP09JN08.001
XIV. Control Rules
Control rules are harvest strategies that specify how a stock's or
stock complex's catch will be modified in response to one or more
factors, particularly estimated stock size. The current NS1 guidelines
include MSY control rules which are ``limit'' control rules and OY
control rules which are ``target'' control rules. For any stock, the
limit control rule results in a higher amount than the target control
rule for a given stock abundance. Because of the new MSA requirement
for annual catch limits to end and prevent overfishing for stocks in a
fishery, NMFS proposes that MSY control rules be replaced by ABC
control rules and become the new limit control rule, and OY control
rules be replaced by ACT control rules and become the new target
control rule. This would align the control rules more directly with the
new requirement to specify an ABC and an ACL for stocks in the fishery
(see earlier discussion in the preamble for the relationship between
OFL and MSY, and between ACT and OY).
ABC and ACT control rules should be developed for each stock when
possible. For stock complexes, ABC and ACT control rules should be
developed for each indicator stock or for the stock complex as a whole.
ACTs should be set with the intention that they typically will be
achieved. A stock's or stock complex's ACT control rule should result
in lower target catches than the ABC control rule would, for all levels
of a stock's or stock complex's abundance.
In the proposed revisions to NS1 guidelines, an ABC control rule is
a specified approach to setting the ABC for a stock or stock complex as
a function of the scientific uncertainty in the estimate of OFL. An ACT
control rule is an approach to setting the ACT for each stock and stock
complex such that the risk of exceeding ACL due to management
uncertainty (ability to control catch and variability in catch data) is
an acceptably low level. Both control rules are designed to reduce the
risk that overfishing will occur.
For rebuilding stocks, the ABC, ACL, and ACT should be set at lower
levels than for rebuilt stocks because two
[[Page 32535]]
objectives are combined. First, overfishing should not occur; and
second, rebuilding at a rate commensurate with the stock's rebuilding
plan should occur. This means that, for a rebuilding stock, a lower
target fishing mortality rate may be needed to accomplish rebuilding,
in addition to avoiding overfishing (i.e., ACL and ACT are lower than
they would be if the stock was rebuilt).
XV. Sector ACLs, ACTs, and AMs
A Council may decide, but is not required, to divide the ACL into
sector-ACLs. ``Sector'' for purposes of the NS1 guidelines means a
distinct user group to which separate management strategies and catch
quotas apply. Examples of sectors could include the commercial sector,
recreational sector, or various gear groups within a fishery. It is up
to each Council to decide how to designate sectors, if any. If sector-
ACLs are established, sector-AMs and sector-ACTs must be developed for
each sector-ACL. In cases where states cooperatively manage a stock, it
is possible that a sector ACL could be further subdivided in order to
establish ``subsector'' ACLs and ACTs for various states to align with
current management of catch limits or quotas in the state fisheries.
The system of ACLs and AMs must be effective and equitable and protect
the stock as a whole from overfishing. The sum of a stock's sector-ACLs
must not exceed the stock's ACL. If sector-ACLs and sector-AMs are
established, additional AMs at the stock level would also be
appropriate. A sector must be closed inseason if timely catch data
indicates its ACL has been reached. If a sector does not have timely
inseason fisheries data, or has a history of annual overages, then a
Council should establish a large enough difference between a sector's
ACT and ACL to improve the probability that the sector-ACL and the
stock's ACL are not exceeded.
XVI. Accountability Measures
AMs are management controls implemented for stocks such that
exceeding the ACL or sector-ACL is prevented, where possible, and
corrected or mitigated if it occurs (see Sec. 600.310(g) of this
proposed action). AMs include: (1) Those that are applied inseason and
designed to prevent the ACL from being reached; (2) measures applied
after the fishing year that are designed to address the operational
issue that caused the ACL overage, ensuring it does not happen in
subsequent fishing years, and, as necessary, address any biological
harm to the stock; and (3) those based on multi-year average data which
are still reviewed and applied annually (see discussion below). AMs
should address and minimize both the frequency of overages and the
magnitude of an overage. AMs should be designed so that if an ACL is
exceeded, specific adjustments are effective in the next fishing year,
or as soon as possible, with explanation of why more timely adjustment
is not possible.
If timely inseason fishery catch data are available for a stock,
Councils should ensure their FMPs contain inseason closure authority as
an AM to prevent a stock's ACL from being exceeded. Where fishery catch
data are not timely enough to implement inseason AMs, the ACT should be
adjusted downward from the ACL to account for the increased management
uncertainty and the delayed ability to implement AMs.
A ``multiyear plan'' as referenced in section 303(a)(15) of the MSA
is a plan that establishes harvest specifications or harvest guidelines
for each year of a time period greater than one year. Because
``multiyear plans'' establish ACLs and ACTs for more than one year at a
time, they should include AMs that provide if an ACL is exceeded in one
year, then a subsequent year's harvest specification (including ACLs
and ACTs) could be revised (see Sec. 600.310(f)(5)(i) of this proposed
action).
Some fisheries have highly variable annual catches and lack
reliable inseason or annual data on which to base AMs. If there are
insufficient data upon which to compare catch to ACL, either inseason
or on an annual basis, a Council could base AMs on comparison of
average catch to average ACL over a three-year moving average period
or, if supported by analysis, some other appropriate multi-year period
(see Sec. 600.310(g)(4) of this proposed action). As a performance
standard, if the average catch exceeds the average ACL more than once
in the last four years, then the ACL, ACT and AM system should be re-
evaluated to improve its performance. The initial ACL and management
measures should incorporate information from previous years so that AMs
based on average ACLs can be applied from the first year.
If a stock is in a rebuilding plan and its ACL is exceeded, the AMs
should include overage adjustments that reduce the ACL in the next
fishing year by the full amount of the overage, unless the best
scientific information available shows that a reduced overage
adjustment is sufficent, or no adjustment is needed to mitigate the
effects of the overage. This AM is important to increase the likelihood
that the stock will continue to rebuild.
As discussed earlier, stocks and stock complexes in federal FMPs
that have a large majority of harvest in state or territorial waters
should have an ACL that takes into consideration the overall status of
the stock. However, federal management would be limited to that portion
of the fishery under federal jurisdiction. Options for AMs that a
Council could consider for stocks or stock complexes caught mostly in
state or territorial waters would include, but are not limited to: (1)
Close the EEZ when the federal portion of the ACL is reached, or (2)
close the EEZ when the overall stock or stock complex's ACL is reached.
The AMs should ensure that federal managers are doing as much as
possible to end and prevent overfishing. When stocks are co-managed by
federal, state, tribal, and/or territorial fishery managers, the goal
should be to develop collaborative conservation and management
strategies, and scientific capacity to support such strategies, to
prevent overfishing of shared stocks and ensure their sustainability.
XVII. Summary of Items To Include in FMPs
This section provides a summary of items that Councils should
include in their FMPs and FMP amendments in order to address ACL, AM,
and other aspects of the proposed NS1 guidelines. Some items are
specific to new MSRA provisions. Others were required prior to MSRA,
but are included here so as to be comprehensive. Councils may review
their FMPs to decide if all stocks are ``in the fishery'' or whether
some fit the category of ``ecosystem component species'' and amend
their FMP as appropriate. If they do not establish EC species through
an FMP amendment, then all stocks in an FMP are presumed to be ``in the
fishery.'' For all stocks and stock complexes that are in the fishery,
the Councils should evaluate and describe the following items in their
FMPs and amend the FMPs, if necessary, to align their management
objectives to end or prevent overfishing (see Sec. 600.310(c) of this
proposed action): (1) MSY and SDC, (2) OY at the stock, stock complex
or fishery level, (3) ABC control rule, (4) ACLs and mechanisms for
setting ACLs and possible sector-specific ACLs in relationship to the
ABC, (5) ACT control rule, (6) AMs and AM mechanisms, and (7) stocks
and stock complexes that have statutory exceptions from ACLs or fall
under limited circumstances which require different approaches to meet
the ACL requirements (e.g., ESA-listed
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stocks and harvests from aquaculture facilities).
The Councils should evaluate the extent to which their FMPs comply
with requirements to define MSY and OY for stocks in the fishery, and
the reasons that OY is reduced from MSY (see Sec. 600.310(e)(3)(iv) of
this proposed action). An overall objective of management of federal
fisheries under the MSA is to conserve fishery resources so as to
prevent overfishing and achieve OY (see sections 2(a)(6) and 2(b)(4) of
the MSA). OY is based on MSY for a fishery, as reduced for economic,
social, or ecological reasons (see section 3(33)(B) of the MSA).
Therefore, it is important that all FMPs have MSY and OY prescribed
correctly.
FMPs should contain a description of fisheries data for the stocks,
stock complexes, and ecosystem component species. The sources of
fishing mortality, such as commercial catch (both landed and
discarded), recreational catch, and bycatch in other fisheries should
be listed in the FMP for each fishery, along with a description of the
data collection and estimation methods used to quantify total catch
mortality in each fishery. The description of the data collection
methods used to monitor the fishery should include information on the
frequency that those data are collected and updated and the scope of
sampling coverage for the fishery. In addition, the FMP should describe
how those data are used to determine the relationship between total
catch at a given point in time and the ACL for a stock or stock
complex.
FMPs should explain issues related to shared jurisdiction of stocks
(if any), and the degree to which ACLs and AMs established by the
Councils will ensure that overfishing does not occur on the stock as a
whole.
NMFS is aware that existing FMPs may use terms that are similar to,
associated with, or may be equivalent to ABC, ACL, ACT, and AM in many
fisheries for which annual specifications are set for different stocks
or stock complexes. NMFS' preference is that, as Councils revise their
FMPs, they use the same terms as set forth in the NS1 guidelines as
finalized. However, given the longstanding use of terms under certain
FMPs, if changing terminology could cause confusion, Councils could opt
to retain existing terminology and explain in a proposed rule how the
terminology and approaches in the FMPs are consistent with those set
forth in the NS1 guidelines.
Councils should amend their FMPs to provide explicit narrative of
how the FMP objectives and annual management measures will work with
ACLs and AMs. All stocks and stock complexes should have an annual or
multiyear specification process for stocks managed in a fishery. An
annual or multiyear specification process for setting or adjusting ACLs
provides a timely, consistent method that the public and stakeholders
can understand, and that provides an opportunity for public comment.
Such a process could also provide a method for assigning an ACL, ACT,
and AM to a ``stock having a life cycle of approximately one year''
that is undergoing overfishing.
XVIII. Change in Timetable When Establishing a Rebuilding Plan
The MSA provides that the Secretary shall annually identify stocks
and stock complexes that are overfished or approaching a condition of
being overfished; notify the appropriate Council at any time when a
stock or stock complex is determined to be overfished; and notify the
appropriate Council when adequate pr