Fisheries Off West Coast States; West Coast Salmon Fisheries; Management Reference Point Updates for Three Stocks of Pacific Salmon, 14066-14069 [2015-06144]
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Federal Register / Vol. 80, No. 52 / Wednesday, March 18, 2015 / Proposed Rules
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[FR Doc. 2015–06153 Filed 3–17–15; 08:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 660
[Docket No. 150227200–5200–01]
RIN 0648–BE79
Fisheries Off West Coast States; West
Coast Salmon Fisheries; Management
Reference Point Updates for Three
Stocks of Pacific Salmon
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule; request for
comments.
wreier-aviles on DSK5TPTVN1PROD with PROPOSALS
AGENCY:
NMFS proposes updates to
management reference point values for
Southern Oregon coastal Chinook
salmon, Grays Harbor fall Chinook
salmon, and Willapa Bay natural coho,
as recommended by the Pacific Fishery
Management Council (Council) for use
in developing annual management
SUMMARY:
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3/18/15 [Insert Federal
Register citation].
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Provisions of the 2010 PM2.5 PSD—Increments,
SILs and SMCs rule (75 FR 64865, October 20,
2010) relating to SILs and SMCs that were affected by the January 22, 2013 U.S. Court of
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the Clean Unit Exemption and Pollution Control
Projects are not SIP approved.
In addition, we have not approve Missouri’s rule
incorporating EPA’s 2007 revision fo the definition of ‘‘chemical processing plants’’ (the ‘‘Ethanol Rule,’’ 72 FR 24060 (May 1, 2007).
Although exemptions previously listed in 10 CSR
10–6.060 have been transferred to 10 CSR 10–
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livestock handling systems from which the only
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measures beginning in 2015. This
update is implemented as part of the
2014 methodology review where the
Council and its advisory bodies
considered new information on the
three stocks of salmon to make a
determination on whether changes to
reference points for these stocks were
warranted.
DATES: Comments on this proposed rule
must be received on or before April 2,
2015.
ADDRESSES: You may submit comments,
identified by NOAA–NMFS–2015–0014,
by any one of the following methods:
• Electronic Submissions: Submit all
electronic public comments via the
Federal e-Rulemaking Portal. Go to
www.regulations.gov/
#!docketDetail;D=NOAA-NMFS-20150014, click the ‘‘Comment Now!’’ icon,
complete the required fields, and enter
or attach your comments.
• Mail: William W. Stelle, Jr.,
Regional Administrator, West Coast
Region, NMFS, 7600 Sand Point Way
NE., Seattle, WA 98115–0070.
Instructions: Comments must be
submitted by one of the above methods
to ensure that the comments are
received, documented, and considered
by NMFS. Comments sent by any other
method, to any other address or
individual, or received after the end of
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*
*
the comment period, may not be
considered. All comments received are
a part of the public record and will
generally be posted for public viewing
on https://www.regulations.gov without
change. All personal identifying
information (e.g., name, address, etc.)
submitted voluntarily by the sender will
be publicly accessible. Do not submit
confidential business information or
otherwise sensitive or protected
information. NMFS will accept
anonymous comments (enter N/A in the
required fields if you wish to remain
anonymous).
FOR FURTHER INFORMATION CONTACT:
Peggy Mundy at 206–526–4323.
SUPPLEMENTARY INFORMATION:
Background
The Council manages West Coast
ocean salmon fisheries under the Pacific
Coast Salmon Fishery Management Plan
(FMP). The FMP has long used stockspecific conservation objectives to
manage fishery impacts to Councilmanaged salmon stocks. Conservation
objectives are, generally, fixed
quantities intended to provide the
necessary guidance during the course of
the annual preseason planning process
to establish salmon fishing seasons that
achieve optimum yield. Under the FMP,
conservation objectives can be added or
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Federal Register / Vol. 80, No. 52 / Wednesday, March 18, 2015 / Proposed Rules
changed either through a plan
amendment or notice and comment
rulemaking if a comprehensive
technical review of the best scientific
information available provides evidence
that, in the view of the Salmon
Technical Team (STT), Scientific and
Statistical Committee (SSC), and the
Council, justifies a modification (FMP
section 3.2.2).
In 2009, NMFS amended the
guidelines for National Standard 1
(NS1) of the Magnuson-Stevens Fishery
Conservation and Management Act
(MSA) at 50 CFR 600.310 to provide
guidance on how to comply with new
annual catch limit (ACL) and
accountability measure requirements for
ending overfishing of fisheries managed
by Federal fishery management plans,
including status determination criteria
(SDC) (74 FR 3204). Amendment 16 to
the FMP (76 FR 81851) defined a suite
of reference points for salmon,
consistent with the revised NS1
guidelines. In the FMP, SDC are defined
in terms of quantifiable, biologicallybased reference points, or population
parameters, including: maximum
sustainable yield (MSY), MSY fishing
mortality rate (FMSY), MSY spawner
abundance (SMSY), minimum stock size
threshold (MSST), and maximum
fishery mortality threshold (MFMT,
generally equal to FMSY). Under the
FMP, changes to SDC can be made
without a plan amendment if a
comprehensive technical review of the
best scientific information available
provides evidence that, in the view of
the STT, SSC, and the Council, a
modification of the values of the SDC is
justified (FMP section 3.1.7).
As part of the 2014 methodology
review, the Council and its advisory
bodies considered new information on
three stocks of salmon (Southern Oregon
coastal Chinook salmon, Grays Harbor
fall Chinook salmon, and Willapa Bay
natural coho) to make a determination
on whether changes to reference points
for these stocks were warranted. A joint
methodology review was conducted by
the STT, SSC, and the Model Evaluation
Workgroup at the Council offices in
Portland, OR, October 21–23, 2014. The
results of the methodology review were
presented at the Council meeting in
Costa Mesa, CA, November 12–19, 2014.
Both the methodology review and the
Council meeting were open to the
public and were announced in the
Federal Register (79 FR 59741, October
3, 2014 and 79 FR 63900, October 27,
2014). Documents considered by the
Council are available on the Council
Web site (https://www.pcouncil.org/
resources/archives/briefing-books/
november-2014-briefing-book/
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#salmonNov2014). The Council
transmitted their recommended changes
to NMFS in a letter dated January 23,
2015. This proposed rule describes the
reference point updates that are being
proposed for implementation in the
FMP in developing annual management
measures beginning in 2015.
Southern Oregon Coastal Chinook
Salmon
The Southern Oregon coastal Chinook
salmon stock, a component of the
Southern Oregon Northern California
Chinook stock complex, is an aggregate
of natural and hatchery fall and spring
Chinook salmon populations in Oregon
streams south of the Elk River (e.g.,
Rogue River, Pistol River, and Chetco
River), plus spring Chinook salmon
from the Umpqua River. Rogue River
fall Chinook are used to indicate relative
abundance of Southern Oregon coastal
Chinook salmon. The current
conservation objective for this stock is
60–90 fish per mile in three standard
index areas. At the 2014 methodology
review, the Oregon Department of Fish
and Wildlife (ODFW) provided an
analysis that was used by the State of
Oregon in 2013 to adopt new State
management objectives for Rogue River
fall Chinook. The analysis used a Ricker
spawner-recruit relationship for Rogue
River fall Chinook that included smolt
survival and mean summer flow
covariates. ODFW proposed that the
Council adopt their conservation
objective and reference points for
Southern Oregon coastal Chinook
salmon in the FMP, while keeping this
stock as a component of the Southern
Oregon Northern California stock
complex (where Klamath River fall
Chinook is the indicator stock). ODFW’s
spawner-recruit analysis resulted in an
SMSY point estimate of 34,992 and FMSY
of 54 percent. ODFW used the 75th
percentile of the SMSY posterior
distribution (36,880 natural-area
spawners) as an estimate of SMSY to
determine an MSST of 18,440 naturalorigin spawners (MSST = 0.5 * 36,880).
ODFW also proposed a stock
conservation objective of 41,000
naturally-produced adults passing
Huntley Park in the Rogue River, near
Gold Beach, OR.
The STT and SSC evaluated ODFW’s
analysis and recommended that the
Council adopt ODFW’s proposed values
as described above. The SSC
recommended ODFW’s proposed values
for SMSY and FMSY but noted that the
choice of MSST, above 50 percent of
SMSY, was a policy decision. Based on
information from the 2014 methodology
review and the advisory body
recommendations, the Council adopted
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the following reference point value
updates for southern Oregon coastal
Chinook salmon and NMFS proposes to
implement them:
• Conservation objective: 41,000
naturally-produced adults passing
Huntley Park
• SMSY 34,992 natural-area spawners
• MFMT (FMSY): 54 percent
• MSST: 18,440 (20,500 measured at
Huntley Park) natural-origin spawners
Grays Harbor Fall Chinook Salmon
During the 2014 methodology review,
Washington Department of Fish and
Wildlife (WDFW) staff presented a
spawner-recruit analysis for Grays
Harbor fall Chinook salmon. The
analysis produced an estimated SMSY of
13,326 for the Chehalis and Humptulips
Rivers combined (9,753 and 3,573,
respectively). This estimate is slightly
lower than the current management
objective of 14,600 natural-area
spawners, which was adopted in 1979
based on available spawning habitat.
The new SMSY estimate of 13,326 is
currently being used by the Pacific
Salmon Commission; adoption by the
Council provides consistency between
the FMP and the Pacific Salmon Treaty.
The STT and SSC agreed that WDFW’s
estimate of SMSY represents the best
available science, and recommended
that the Council adopt this estimate of
SMSY, and associated reference points
developed by the STT, for the salmon
FMP.
Based on information from the 2014
methodology review and the advisory
body recommendations, the Council
adopted the recommended stock
productivity methodology and the
resulting SMSY value. However, the
Council’s action was not explicit with
respect to the values for the associated
reference points, specifically MSST and
MFMT. The Council and NMFS use
MSST to determine if a stock is
overfished, and MFMT to determine if
overfishing is occurring. Because it is
necessary to make determinations as to
whether the Grays Harbor fall Chinook
salmon stock is overfished or
experiencing overfishing in preparation
for the development of the 2015
management measures, NMFS is
proposing to implement values for
MSST and MFMT based on the
recommendations of the STT, pursuant
to NMFS’ independent rulemaking
authority (18 U.S.C. 1855(d)). Should
the Council choose to adopt a different
value for MSST or MFMT, NMFS will
determine the appropriate process for
considering those values. The FMP
states that MSST is generally defined as
0.5 * SMSY or 0.75 * SMSY, although
there are some exceptions. Currently,
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MSST for Grays Harbor fall Chinook is
MSST = 0.5 * SMSY. Applying the same
approach to the proposed SMSY value of
13,326 results in an MSST of 6,663
natural-area spawners. Applying the
spawner-recruit parameter estimates
from WDFW’s analysis, as
recommended by the STT as the best
available science, yields an MFMT of 63
percent. Therefore, based on the
recommendation of the Council and the
advisory bodies, NMFS proposes the
following reference point value updates
for Grays Harbor fall Chinook salmon:
• Conservation objective: 13,326
spawners (equal to SMSY, per FMP
section 3.2.1)
• SMSY: 13,326 spawners (9,753 in the
Chehalis River and 3,573 in the
Humptulips River)
• MFMT (FMSY): 63 percent (application
of WDFW’s spawner-recruit analysis
as recommended by the STT)
• MSST: 6,663 natural-area spawners
(MSST = 0.5 * SMSY) (application of
current policy to updated SMSY).
Willapa Bay Natural Coho
The Willapa Bay natural coho salmon
stock was added to the FMP under
Amendment 16, but without a
conservation objective and other
reference point values. WDFW’s habitatbased escapement goal (i.e., adult
salmon escaping the fishery to return to
freshwater habitat for spawning) for this
stock is 13,090 natural-origin fish. The
STT performed a spawner-recruit
analysis, which produced an estimated
SMSY of 17,200 natural-area spawners,
and an FMSY of 74 percent. The STT
recommended that the Council adopt
reference points for this stock based on
this analysis. The STT’s
recommendation also included an
MFMT of 74 percent, a MSST of 8,600
natural-area spawners (MSST = 0.5 *
SMSY), and annual catch limit calculated
on the basis of FACL = 0.95 * FMSY = 71
percent. The SSC supported these
recommendations.
Based on information from the 2014
methodology review and the advisory
body recommendations, the Council
adopted the recommended stock
productivity methodology and the
resulting SMSY and MFMT values.
However, the Council’s action was not
explicit with respect to the value for
MSST. The Council and NMFS use
MSST to determine if a stock is
overfished. Because it is necessary to
determine whether the Willapa Bay
natural coho stock is overfished, in
preparation for the development of the
2015 management measures, NMFS is
proposing to implement a value for
MSST based on the recommendations of
the STT, pursuant to NMFS’
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independent rulemaking authority (18
U.S.C. 1855(d)). Should the Council
choose to adopt a different value for
MSST, it should confer with NMFS
regarding the appropriate process for
addressing this value. As noted above,
the FMP states that MSST is generally
defined as 0.5 * SMSY or 0.75 * SMSY.
The Council has generally applied a
policy of MSST = 0.5* SMSY. Applying
this approach to the proposed SMSY
value of 17,200 results in an MSST of
8,600 natural-area spawners. Therefore,
based on the recommendation of the
Council and the advisory bodies, NMFS
proposes the following reference point
values for Willapa Bay natural coho:
• Conservation objective: 17,200
natural-area spawners (equal to SMSY,
per FMP section 3.2.1)
• SMSY: 17,200 natural-area spawners
• MFMT (FMSY): 74 percent
• MSST: 8,600 natural-area spawners
(MSST = 0.5 * SMSY)
In addition, because Willapa Bay
natural coho is not managed under an
international agreement, listed under
the ESA, or designated as a hatchery
stock, the FMP requires that it be
managed with an ACL (FMP sections
3.3.3 and 3.3.4). Because it is not part
of a stock complex, it will be managed
using an individual stock ACL. The
Council and NMFS will determine the
ACL annually, based on annual
abundance projections and the
appropriate formula set forth in the FMP
(FMP section 3.3.4). Because the
Council has recommended, and NMFS
proposes to adopt, a directly estimated
value for FMSY, Willapa Bay natural
coho is a Tier 1 stock for purposes of
determining the acceptable biological
catch (ABC) and the ACL. According to
the FMP, for a Tier 1 stock, FABC = FMSY
* 0.95, FABC = FACL, and FACL is applied
to the projected annual abundance to
determine the ACL escapement level for
the year (FMP sections 3.3.3 and 3.3.4).
As noted earlier, the Council is
expected to address the reference points
for Willapa Bay natural coho salmon
that were not explicit in its prior action
at its March meeting. It is possible that
it could recommend values for MSST
that are different from those proposed
above. Were this to occur, the
recommended values would likely be
0.75 * SMSY or between that value and
0.5 * SMSY, based on the definition of
MSST set forth in the FMP.
Classification
Pursuant to section 304(b)(1)(A) of the
MSA, the NMFS Assistant
Administrator has determined that this
proposed rule is consistent with the
Pacific Salmon Fishery Management
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Plan, the MSA, and other applicable
law, subject to further consideration
after public comment. As described
above, NMFS is proposing portions of
this rule according to section 305(d) of
the MSA.
This proposed rule has been
determined to be not significant for
purposes of Executive Order 12866.
The West Coast Regional
Administrator has determined that the
actions of this proposed rule qualify for
categorical exclusion from further NEPA
analysis under NAO 216–6.
The Chief Counsel for Regulation of
the Department of Commerce certified
to the Chief Counsel for Advocacy of the
Small Business Administration that this
proposed rule, if adopted, would not
have a significant economic impact on
a substantial number of small entities.
The purpose of the Regulatory
Flexibility Act (RFA) is to relieve small
businesses, small organizations, and
small governmental entities of
burdensome regulations and recordkeeping requirements. Major goals of the
RFA are: (1) To increase agency
awareness and understanding of the
impact of their regulations on small
business, (2) to require agencies
communicate and explain their findings
to the public, and (3) to encourage
agencies to use flexibility and to provide
regulatory relief to small entities. The
RFA emphasizes predicting impacts on
small entities as a group distinct from
other entities and the consideration of
alternatives that may minimize the
impacts while still achieving the stated
objective of the action. An initial
regulatory flexibility analysis (IRFA) is
conducted unless it is determined that
an action will not have a ‘‘significant
economic impact on a substantial
number of small entities.’’
The objective of this proposed rule is
to update management reference points
for three stocks of salmon under the
FMP. This proposed rule would impact
vessels harvesting salmon from the
ocean troll fishery. The following
fishery information is found in the
Council’s Review of 2013 Ocean Salmon
Fisheries Stock Assessment and
Fisheries Evaluation Document. In 2013,
there were 2,270 permits issued for this
fishery, with a total ex-vessel value of
$34.1 million. Of the 2,270 permits,
only 1,177 actually landed salmon all
within the states of California, Oregon
and Washington. In California, 670
vessels landed salmon for an ex-vessel
value of $23.6 million; in Oregon, 399
vessels landed salmon for an ex-vessel
value of $7.6 million; and in
Washington, 108 vessels landed salmon
for an ex-vessel value of $2.8 million.
Treaty Indian ocean fisheries landed
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salmon with an ex-vessel value of $6.4
million.
On June 12, 2014, the Small Business
Administration (SBA) issued an interim
final rule revising the small business
size standards for several industries
effective July 14, 2014 (79 FR 33467
(June 12, 2014)). The rule increased the
size standard from $19.0 to $20.5
million for finfish fishing, from $5 to
$5.5 million for shellfish fishing, and
from $7.0 million to $7.5 million for
other marine fishing, for-hire
businesses, and marinas. Based on this
size standard, all 1,177 vessels that
landed salmon from the ocean troll
fishery are considered small under the
Small Business Administration
approved definition of a small fish
harvester. Therefore, there are no
disproportionate impacts between small
and large vessels. Furthermore, there are
no disproportionate impacts based on
homeport, gear type, or vessel size from
the promulgation of this proposed rule.
This proposed rule would not result
in any immediate impacts on revenues
or costs for the small entities
participating in the Pacific salmon
fishery; the updated management
reference point values will be
considered within the overall suite of
criteria that are used to frame the annual
management measures. The
management reference points are used
to set Council management goals,
identify when overfishing is occurring,
and identify when a stock is overfished.
These values all have the potential to
impact how annual salmon management
measures are structured, specifically
what constraints are needed to manage
impacts. However, the salmon fishery
impacts a large number of stocks, and
the fishery as a whole must be managed
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to meet management goals for every
stock. Depending on abundance
projections for a given year, meeting
management goals for a few particularly
limiting stocks typically results in
fisheries that are not limited by
management goals for the remaining
stocks. Therefore, the proposed changes
would only impact fishery revenues in
years when any of the three affected
salmon stocks are constraining to
fisheries, which is unlikely based on
historical data.
As a result, an IRFA is not required
and none has been prepared. NMFS will
conduct the appropriate analyses for
any subsequent rulemakings stemming
from this proposed rule.
This proposed rule would not
establish any new reporting or
recordkeeping requirements. This
proposed rule does not include a
collection of information. No Federal
rules have been identified that
duplicate, overlap, or conflict with this
action.
This action is not expected to have
adverse effects on any species listed
under the Endangered Species Act
(ESA) or designated critical habitat. This
action modifies reference points used in
the setting of annual management
measures for West Coast salmon
fisheries. NMFS has current ESA
biological opinions that cover fishing
under annual regulations adopted under
the FMP on all listed salmon species.
NMFS reiterates their consultation
standards for all ESA-listed salmon and
steelhead species in their annual
Guidance letter to the Council. Some of
NMFS past biological opinions have
found no jeopardy, and others have
found jeopardy, but provided reasonable
and prudent alternatives to avoid
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14069
jeopardy. The annual management
measures are designed to be consistent
with the biological opinions that found
no jeopardy, and with the reasonable
and prudent alternatives in the jeopardy
biological opinions. The Council’s
recommended management measures,
which will be consistent with the
reference points proposed here,
therefore comply with NMFS’
consultation standards and guidance for
all listed salmon species which may be
affected by Council fisheries. In some
cases, the recommended measures are
more restrictive than NMFS’ ESA
requirements.
In 2009, NMFS consulted on the
effects of fishing under the Salmon FMP
on the endangered Southern Resident
Killer Whale Distinct Population
Segment (SRKW) and concluded the
salmon fisheries were not likely to
jeopardize SRKW. Annual salmon
management measures are designed to
be consistent with the terms of that
biological opinion.
This proposed rule was developed
after meaningful collaboration with the
affected tribes, through the Council
process. Under the MSA at 16 U.S.C.
1852(b)(5), one of the voting members of
the Council must be a representative of
an Indian Tribe with Federally
recognized fishing rights from the area
of the Council’s jurisdiction.
Authority: 16 U.S.C. 1801 et seq.
Dated: March 12, 2015.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
[FR Doc. 2015–06144 Filed 3–17–15; 8:45 am]
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[Federal Register Volume 80, Number 52 (Wednesday, March 18, 2015)]
[Proposed Rules]
[Pages 14066-14069]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2015-06144]
=======================================================================
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 660
[Docket No. 150227200-5200-01]
RIN 0648-BE79
Fisheries Off West Coast States; West Coast Salmon Fisheries;
Management Reference Point Updates for Three Stocks of Pacific Salmon
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Proposed rule; request for comments.
-----------------------------------------------------------------------
SUMMARY: NMFS proposes updates to management reference point values for
Southern Oregon coastal Chinook salmon, Grays Harbor fall Chinook
salmon, and Willapa Bay natural coho, as recommended by the Pacific
Fishery Management Council (Council) for use in developing annual
management measures beginning in 2015. This update is implemented as
part of the 2014 methodology review where the Council and its advisory
bodies considered new information on the three stocks of salmon to make
a determination on whether changes to reference points for these stocks
were warranted.
DATES: Comments on this proposed rule must be received on or before
April 2, 2015.
ADDRESSES: You may submit comments, identified by NOAA-NMFS-2015-0014,
by any one of the following methods:
Electronic Submissions: Submit all electronic public
comments via the Federal e-Rulemaking Portal. Go to
www.regulations.gov/#!docketDetail;D=NOAA-NMFS-2015-0014, click the
``Comment Now!'' icon, complete the required fields, and enter or
attach your comments.
Mail: William W. Stelle, Jr., Regional Administrator, West
Coast Region, NMFS, 7600 Sand Point Way NE., Seattle, WA 98115-0070.
Instructions: Comments must be submitted by one of the above
methods to ensure that the comments are received, documented, and
considered by NMFS. Comments sent by any other method, to any other
address or individual, or received after the end of the comment period,
may not be considered. All comments received are a part of the public
record and will generally be posted for public viewing on https://www.regulations.gov without change. All personal identifying
information (e.g., name, address, etc.) submitted voluntarily by the
sender will be publicly accessible. Do not submit confidential business
information or otherwise sensitive or protected information. NMFS will
accept anonymous comments (enter N/A in the required fields if you wish
to remain anonymous).
FOR FURTHER INFORMATION CONTACT: Peggy Mundy at 206-526-4323.
SUPPLEMENTARY INFORMATION:
Background
The Council manages West Coast ocean salmon fisheries under the
Pacific Coast Salmon Fishery Management Plan (FMP). The FMP has long
used stock-specific conservation objectives to manage fishery impacts
to Council-managed salmon stocks. Conservation objectives are,
generally, fixed quantities intended to provide the necessary guidance
during the course of the annual preseason planning process to establish
salmon fishing seasons that achieve optimum yield. Under the FMP,
conservation objectives can be added or
[[Page 14067]]
changed either through a plan amendment or notice and comment
rulemaking if a comprehensive technical review of the best scientific
information available provides evidence that, in the view of the Salmon
Technical Team (STT), Scientific and Statistical Committee (SSC), and
the Council, justifies a modification (FMP section 3.2.2).
In 2009, NMFS amended the guidelines for National Standard 1 (NS1)
of the Magnuson-Stevens Fishery Conservation and Management Act (MSA)
at 50 CFR 600.310 to provide guidance on how to comply with new annual
catch limit (ACL) and accountability measure requirements for ending
overfishing of fisheries managed by Federal fishery management plans,
including status determination criteria (SDC) (74 FR 3204). Amendment
16 to the FMP (76 FR 81851) defined a suite of reference points for
salmon, consistent with the revised NS1 guidelines. In the FMP, SDC are
defined in terms of quantifiable, biologically-based reference points,
or population parameters, including: maximum sustainable yield (MSY),
MSY fishing mortality rate (FMSY), MSY spawner abundance
(SMSY), minimum stock size threshold (MSST), and maximum
fishery mortality threshold (MFMT, generally equal to FMSY).
Under the FMP, changes to SDC can be made without a plan amendment if a
comprehensive technical review of the best scientific information
available provides evidence that, in the view of the STT, SSC, and the
Council, a modification of the values of the SDC is justified (FMP
section 3.1.7).
As part of the 2014 methodology review, the Council and its
advisory bodies considered new information on three stocks of salmon
(Southern Oregon coastal Chinook salmon, Grays Harbor fall Chinook
salmon, and Willapa Bay natural coho) to make a determination on
whether changes to reference points for these stocks were warranted. A
joint methodology review was conducted by the STT, SSC, and the Model
Evaluation Workgroup at the Council offices in Portland, OR, October
21-23, 2014. The results of the methodology review were presented at
the Council meeting in Costa Mesa, CA, November 12-19, 2014. Both the
methodology review and the Council meeting were open to the public and
were announced in the Federal Register (79 FR 59741, October 3, 2014
and 79 FR 63900, October 27, 2014). Documents considered by the Council
are available on the Council Web site (https://www.pcouncil.org/resources/archives/briefing-books/november-2014-briefing-book/#salmonNov2014). The Council transmitted their recommended changes to
NMFS in a letter dated January 23, 2015. This proposed rule describes
the reference point updates that are being proposed for implementation
in the FMP in developing annual management measures beginning in 2015.
Southern Oregon Coastal Chinook Salmon
The Southern Oregon coastal Chinook salmon stock, a component of
the Southern Oregon Northern California Chinook stock complex, is an
aggregate of natural and hatchery fall and spring Chinook salmon
populations in Oregon streams south of the Elk River (e.g., Rogue
River, Pistol River, and Chetco River), plus spring Chinook salmon from
the Umpqua River. Rogue River fall Chinook are used to indicate
relative abundance of Southern Oregon coastal Chinook salmon. The
current conservation objective for this stock is 60-90 fish per mile in
three standard index areas. At the 2014 methodology review, the Oregon
Department of Fish and Wildlife (ODFW) provided an analysis that was
used by the State of Oregon in 2013 to adopt new State management
objectives for Rogue River fall Chinook. The analysis used a Ricker
spawner-recruit relationship for Rogue River fall Chinook that included
smolt survival and mean summer flow covariates. ODFW proposed that the
Council adopt their conservation objective and reference points for
Southern Oregon coastal Chinook salmon in the FMP, while keeping this
stock as a component of the Southern Oregon Northern California stock
complex (where Klamath River fall Chinook is the indicator stock).
ODFW's spawner-recruit analysis resulted in an SMSY point
estimate of 34,992 and FMSY of 54 percent. ODFW used the
75th percentile of the SMSY posterior distribution (36,880
natural-area spawners) as an estimate of SMSY to determine
an MSST of 18,440 natural-origin spawners (MSST = 0.5 * 36,880). ODFW
also proposed a stock conservation objective of 41,000 naturally-
produced adults passing Huntley Park in the Rogue River, near Gold
Beach, OR.
The STT and SSC evaluated ODFW's analysis and recommended that the
Council adopt ODFW's proposed values as described above. The SSC
recommended ODFW's proposed values for SMSY and
FMSY but noted that the choice of MSST, above 50 percent of
SMSY, was a policy decision. Based on information from the
2014 methodology review and the advisory body recommendations, the
Council adopted the following reference point value updates for
southern Oregon coastal Chinook salmon and NMFS proposes to implement
them:
Conservation objective: 41,000 naturally-produced adults
passing Huntley Park
SMSY 34,992 natural-area spawners
MFMT (FMSY): 54 percent
MSST: 18,440 (20,500 measured at Huntley Park) natural-origin
spawners
Grays Harbor Fall Chinook Salmon
During the 2014 methodology review, Washington Department of Fish
and Wildlife (WDFW) staff presented a spawner-recruit analysis for
Grays Harbor fall Chinook salmon. The analysis produced an estimated
SMSY of 13,326 for the Chehalis and Humptulips Rivers
combined (9,753 and 3,573, respectively). This estimate is slightly
lower than the current management objective of 14,600 natural-area
spawners, which was adopted in 1979 based on available spawning
habitat. The new SMSY estimate of 13,326 is currently being
used by the Pacific Salmon Commission; adoption by the Council provides
consistency between the FMP and the Pacific Salmon Treaty. The STT and
SSC agreed that WDFW's estimate of SMSY represents the best
available science, and recommended that the Council adopt this estimate
of SMSY, and associated reference points developed by the
STT, for the salmon FMP.
Based on information from the 2014 methodology review and the
advisory body recommendations, the Council adopted the recommended
stock productivity methodology and the resulting SMSY value.
However, the Council's action was not explicit with respect to the
values for the associated reference points, specifically MSST and MFMT.
The Council and NMFS use MSST to determine if a stock is overfished,
and MFMT to determine if overfishing is occurring. Because it is
necessary to make determinations as to whether the Grays Harbor fall
Chinook salmon stock is overfished or experiencing overfishing in
preparation for the development of the 2015 management measures, NMFS
is proposing to implement values for MSST and MFMT based on the
recommendations of the STT, pursuant to NMFS' independent rulemaking
authority (18 U.S.C. 1855(d)). Should the Council choose to adopt a
different value for MSST or MFMT, NMFS will determine the appropriate
process for considering those values. The FMP states that MSST is
generally defined as 0.5 * SMSY or 0.75 * SMSY,
although there are some exceptions. Currently,
[[Page 14068]]
MSST for Grays Harbor fall Chinook is MSST = 0.5 * SMSY.
Applying the same approach to the proposed SMSY value of
13,326 results in an MSST of 6,663 natural-area spawners. Applying the
spawner-recruit parameter estimates from WDFW's analysis, as
recommended by the STT as the best available science, yields an MFMT of
63 percent. Therefore, based on the recommendation of the Council and
the advisory bodies, NMFS proposes the following reference point value
updates for Grays Harbor fall Chinook salmon:
Conservation objective: 13,326 spawners (equal to
SMSY, per FMP section 3.2.1)
SMSY: 13,326 spawners (9,753 in the Chehalis River
and 3,573 in the Humptulips River)
MFMT (FMSY): 63 percent (application of WDFW's
spawner-recruit analysis as recommended by the STT)
MSST: 6,663 natural-area spawners (MSST = 0.5 *
SMSY) (application of current policy to updated
SMSY).
Willapa Bay Natural Coho
The Willapa Bay natural coho salmon stock was added to the FMP
under Amendment 16, but without a conservation objective and other
reference point values. WDFW's habitat-based escapement goal (i.e.,
adult salmon escaping the fishery to return to freshwater habitat for
spawning) for this stock is 13,090 natural-origin fish. The STT
performed a spawner-recruit analysis, which produced an estimated
SMSY of 17,200 natural-area spawners, and an FMSY
of 74 percent. The STT recommended that the Council adopt reference
points for this stock based on this analysis. The STT's recommendation
also included an MFMT of 74 percent, a MSST of 8,600 natural-area
spawners (MSST = 0.5 * SMSY), and annual catch limit
calculated on the basis of FACL = 0.95 * FMSY =
71 percent. The SSC supported these recommendations.
Based on information from the 2014 methodology review and the
advisory body recommendations, the Council adopted the recommended
stock productivity methodology and the resulting SMSY and
MFMT values. However, the Council's action was not explicit with
respect to the value for MSST. The Council and NMFS use MSST to
determine if a stock is overfished. Because it is necessary to
determine whether the Willapa Bay natural coho stock is overfished, in
preparation for the development of the 2015 management measures, NMFS
is proposing to implement a value for MSST based on the recommendations
of the STT, pursuant to NMFS' independent rulemaking authority (18
U.S.C. 1855(d)). Should the Council choose to adopt a different value
for MSST, it should confer with NMFS regarding the appropriate process
for addressing this value. As noted above, the FMP states that MSST is
generally defined as 0.5 * SMSY or 0.75 * SMSY.
The Council has generally applied a policy of MSST = 0.5*
SMSY. Applying this approach to the proposed SMSY
value of 17,200 results in an MSST of 8,600 natural-area spawners.
Therefore, based on the recommendation of the Council and the advisory
bodies, NMFS proposes the following reference point values for Willapa
Bay natural coho:
Conservation objective: 17,200 natural-area spawners (equal to
SMSY, per FMP section 3.2.1)
SMSY: 17,200 natural-area spawners
MFMT (FMSY): 74 percent
MSST: 8,600 natural-area spawners (MSST = 0.5 *
SMSY)
In addition, because Willapa Bay natural coho is not managed under
an international agreement, listed under the ESA, or designated as a
hatchery stock, the FMP requires that it be managed with an ACL (FMP
sections 3.3.3 and 3.3.4). Because it is not part of a stock complex,
it will be managed using an individual stock ACL. The Council and NMFS
will determine the ACL annually, based on annual abundance projections
and the appropriate formula set forth in the FMP (FMP section 3.3.4).
Because the Council has recommended, and NMFS proposes to adopt, a
directly estimated value for FMSY, Willapa Bay natural coho
is a Tier 1 stock for purposes of determining the acceptable biological
catch (ABC) and the ACL. According to the FMP, for a Tier 1 stock,
FABC = FMSY * 0.95, FABC =
FACL, and FACL is applied to the projected annual
abundance to determine the ACL escapement level for the year (FMP
sections 3.3.3 and 3.3.4).
As noted earlier, the Council is expected to address the reference
points for Willapa Bay natural coho salmon that were not explicit in
its prior action at its March meeting. It is possible that it could
recommend values for MSST that are different from those proposed above.
Were this to occur, the recommended values would likely be 0.75 *
SMSY or between that value and 0.5 * SMSY, based
on the definition of MSST set forth in the FMP.
Classification
Pursuant to section 304(b)(1)(A) of the MSA, the NMFS Assistant
Administrator has determined that this proposed rule is consistent with
the Pacific Salmon Fishery Management Plan, the MSA, and other
applicable law, subject to further consideration after public comment.
As described above, NMFS is proposing portions of this rule according
to section 305(d) of the MSA.
This proposed rule has been determined to be not significant for
purposes of Executive Order 12866.
The West Coast Regional Administrator has determined that the
actions of this proposed rule qualify for categorical exclusion from
further NEPA analysis under NAO 216-6.
The Chief Counsel for Regulation of the Department of Commerce
certified to the Chief Counsel for Advocacy of the Small Business
Administration that this proposed rule, if adopted, would not have a
significant economic impact on a substantial number of small entities.
The purpose of the Regulatory Flexibility Act (RFA) is to relieve
small businesses, small organizations, and small governmental entities
of burdensome regulations and record-keeping requirements. Major goals
of the RFA are: (1) To increase agency awareness and understanding of
the impact of their regulations on small business, (2) to require
agencies communicate and explain their findings to the public, and (3)
to encourage agencies to use flexibility and to provide regulatory
relief to small entities. The RFA emphasizes predicting impacts on
small entities as a group distinct from other entities and the
consideration of alternatives that may minimize the impacts while still
achieving the stated objective of the action. An initial regulatory
flexibility analysis (IRFA) is conducted unless it is determined that
an action will not have a ``significant economic impact on a
substantial number of small entities.''
The objective of this proposed rule is to update management
reference points for three stocks of salmon under the FMP. This
proposed rule would impact vessels harvesting salmon from the ocean
troll fishery. The following fishery information is found in the
Council's Review of 2013 Ocean Salmon Fisheries Stock Assessment and
Fisheries Evaluation Document. In 2013, there were 2,270 permits issued
for this fishery, with a total ex-vessel value of $34.1 million. Of the
2,270 permits, only 1,177 actually landed salmon all within the states
of California, Oregon and Washington. In California, 670 vessels landed
salmon for an ex-vessel value of $23.6 million; in Oregon, 399 vessels
landed salmon for an ex-vessel value of $7.6 million; and in
Washington, 108 vessels landed salmon for an ex-vessel value of $2.8
million. Treaty Indian ocean fisheries landed
[[Page 14069]]
salmon with an ex-vessel value of $6.4 million.
On June 12, 2014, the Small Business Administration (SBA) issued an
interim final rule revising the small business size standards for
several industries effective July 14, 2014 (79 FR 33467 (June 12,
2014)). The rule increased the size standard from $19.0 to $20.5
million for finfish fishing, from $5 to $5.5 million for shellfish
fishing, and from $7.0 million to $7.5 million for other marine
fishing, for-hire businesses, and marinas. Based on this size standard,
all 1,177 vessels that landed salmon from the ocean troll fishery are
considered small under the Small Business Administration approved
definition of a small fish harvester. Therefore, there are no
disproportionate impacts between small and large vessels. Furthermore,
there are no disproportionate impacts based on homeport, gear type, or
vessel size from the promulgation of this proposed rule.
This proposed rule would not result in any immediate impacts on
revenues or costs for the small entities participating in the Pacific
salmon fishery; the updated management reference point values will be
considered within the overall suite of criteria that are used to frame
the annual management measures. The management reference points are
used to set Council management goals, identify when overfishing is
occurring, and identify when a stock is overfished. These values all
have the potential to impact how annual salmon management measures are
structured, specifically what constraints are needed to manage impacts.
However, the salmon fishery impacts a large number of stocks, and the
fishery as a whole must be managed to meet management goals for every
stock. Depending on abundance projections for a given year, meeting
management goals for a few particularly limiting stocks typically
results in fisheries that are not limited by management goals for the
remaining stocks. Therefore, the proposed changes would only impact
fishery revenues in years when any of the three affected salmon stocks
are constraining to fisheries, which is unlikely based on historical
data.
As a result, an IRFA is not required and none has been prepared.
NMFS will conduct the appropriate analyses for any subsequent
rulemakings stemming from this proposed rule.
This proposed rule would not establish any new reporting or
recordkeeping requirements. This proposed rule does not include a
collection of information. No Federal rules have been identified that
duplicate, overlap, or conflict with this action.
This action is not expected to have adverse effects on any species
listed under the Endangered Species Act (ESA) or designated critical
habitat. This action modifies reference points used in the setting of
annual management measures for West Coast salmon fisheries. NMFS has
current ESA biological opinions that cover fishing under annual
regulations adopted under the FMP on all listed salmon species. NMFS
reiterates their consultation standards for all ESA-listed salmon and
steelhead species in their annual Guidance letter to the Council. Some
of NMFS past biological opinions have found no jeopardy, and others
have found jeopardy, but provided reasonable and prudent alternatives
to avoid jeopardy. The annual management measures are designed to be
consistent with the biological opinions that found no jeopardy, and
with the reasonable and prudent alternatives in the jeopardy biological
opinions. The Council's recommended management measures, which will be
consistent with the reference points proposed here, therefore comply
with NMFS' consultation standards and guidance for all listed salmon
species which may be affected by Council fisheries. In some cases, the
recommended measures are more restrictive than NMFS' ESA requirements.
In 2009, NMFS consulted on the effects of fishing under the Salmon
FMP on the endangered Southern Resident Killer Whale Distinct
Population Segment (SRKW) and concluded the salmon fisheries were not
likely to jeopardize SRKW. Annual salmon management measures are
designed to be consistent with the terms of that biological opinion.
This proposed rule was developed after meaningful collaboration
with the affected tribes, through the Council process. Under the MSA at
16 U.S.C. 1852(b)(5), one of the voting members of the Council must be
a representative of an Indian Tribe with Federally recognized fishing
rights from the area of the Council's jurisdiction.
Authority: 16 U.S.C. 1801 et seq.
Dated: March 12, 2015.
Samuel D. Rauch III,
Deputy Assistant Administrator for Regulatory Programs, National Marine
Fisheries Service.
[FR Doc. 2015-06144 Filed 3-17-15; 8:45 am]
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