Fisheries of the Northeastern United States; Atlantic Herring Fishery; 2007-2009 Specifications, 17807-17813 [E7-6648]
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Federal Register / Vol. 72, No. 68 / Tuesday, April 10, 2007 / Rules and Regulations
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recent Vessel Monitoring System (VMS)
reports and other available information,
the Regional Administrator has
determined that the current rate of
harvest will result in the under-harvest
of the GB yellowtail flounder TAC
during the 2006 fishing year. Based on
this information, the Regional
Administrator is increasing the current
10,000–lb (4,536–kg) trip limit in the
Western U.S./Canada Area, and the
5,000–lb (2,268–kg) trip limit in the
Eastern U.S./Canada Area to 25,000 lb
(11,340 kg) in both areas, effective April
5, 2007, through April 30, 2007.
Accordingly, there is a 25,000–lb
(11,340–kg) trip limit on the amount of
GB yellowtail flounder that can be
harvested or landed for the remainder of
the fishing year for vessels subject to
these regulations. GB yellowtail
flounder landings will be closely
monitored through VMS and other
available information. Should 100
percent of the TAC allocation for GB
yellowtail flounder be projected to be
harvested, the Eastern U.S./Canada Area
will close to all groundfish DAS vessels,
and all vessels will be prohibited from
harvesting, possessing, or landing
yellowtail flounder from the U.S./
Canada Management Area for the
remainder of the fishing year.
Additionally, the Eastern GB cod TAC
will also be closely monitored, and
should 100 percent of its TAC allocation
be projected to be harvested, groundfish
DAS vessels will be prohibited from
entering the Eastern U.S./Canada Area
for the remainder of the fishing year, as
required by the regulations at
§ 648.85(a)(3)(iv).
Classification
This action is authorized by 50 CFR
part 648 and is exempt from review
under Executive Order 12866.
Pursuant to 5 U.S.C. 553(b)(B), the
Assistant Administrator (AA) finds good
cause to waive prior notice and
opportunity for public comment for this
action, because notice and comment
would be impracticable and contrary to
the public interest. The regulations at
§ 648.85(a)(3)(iv)(D) grant the Regional
Administrator the authority to adjust the
GB yellowtail flounder trip limits to
prevent over-harvesting or underharvesting the TAC allocation. Given
that approximately 20 percent of the GB
yellowtail flounder TAC remains
unharvested and the 2006 fishing year
ends on April 30, 2007, the time
necessary to provide for prior notice,
opportunity for public comment, or
delayed effectiveness would prevent the
agency from ensuring that the 2006 TAC
for GB yellowtail flounder will be fully
harvested. If implementation of this
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action is delayed, the NE multispecies
fishery could be prevented from fully
harvesting the TAC for GB yellowtail
flounder during the 2006 fishing year.
Under-harvesting the GB yellowtail TAC
would result in increased economic
impacts to the industry and social
impacts beyond those analyzed for
Amendment 13, as the full potential
revenue from the available GB
yellowtail flounder TAC in the U.S./
Canada Management Area would not be
realized. This action also relieves a
restriction placed on the NE
multispecies fishing industry by
liberalizing the trip limits for GB
yellowtail flounder.
For the reasons specified above and
because this action relieves a restriction,
the AA finds good cause, pursuant to 5
U.S.C. 553(d)(3), to waive the entire 30day delayed effectiveness period for this
action. A delay in the effectiveness of
the trip limit modification in this rule
would prevent the agency from meeting
its management obligation and ensuring
the opportunity for the 2006 TAC for GB
yellowtail flounder specified for the
U.S./Canada Management Area to be
harvested at a level that approaches
optimum yield. Any such delay could
lead to the negative impacts to the
fishing industry described above.
The rate of harvest of the GB
yellowtail flounder TAC in the U.S./
Canada Management Area is updated
weekly on the internet at https://
www.nero.noaa.gov. Accordingly, the
public is able to obtain information that
would provide at least some advanced
notice of a potential action to provide
additional opportunities to the NE
multispecies industry to fully harvest
the TAC for GB yellowtail flounder
during the 2006 fishing year. Further,
the potential for this action was
considered and open to public comment
during the development of Amendment
13 and Framework 42. Therefore, any
negative effect the waiving of public
comment and delayed effectiveness may
have on the public is mitigated by these
factors.
Authority: 16 U.S.C. 1801 et seq.
Dated: April 5, 2007.
James P. Burgess
Acting Director, Office of Sustainable
Fisheries, National Marine Fisheries Service.
[FR Doc. 07–1764 Filed 4–5–07; 1:36 pm]
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17807
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 061228342–7068–02; I.D.
122206A]
RIN 0648–AT66
Fisheries of the Northeastern United
States; Atlantic Herring Fishery; 2007–
2009 Specifications
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
SUMMARY: NMFS announces final
specifications for the 2007–2009 fishing
years for the Atlantic herring (herring)
fishery. The intent of this final rule is
to conserve and manage the herring
resource and provide for a sustainable
fishery.
Effective May 10, 2007, through
December 31, 2009.
ADDRESSES: Copies of supporting
documents, including the
Environmental Assessment, Regulatory
Impact Review, Initial Regulatory
Flexibility Analysis (EA/RIR/IRFA), and
Essential Fish Habitat Assessment are
available from Paul J. Howard,
Executive Director, New England
Fishery Management Council, 50 Water
Street, Mill 2, Newburyport, MA 01950.
The EA/RIR/IRFA is also accessible via
the Internet at https://www.nero.gov.
NMFS prepared a Final Final Regulatory
Flexibility Analysis (FRFA), a summary
of which is contained in the
Classification section of the preamble of
this final rule. Copies of the FRFA and
the Small Entity Compliance Guide are
available from Patricia A. Kurkul,
Regional Administrator, Northeast
Region, National Marine Fisheries
Service, One Blackburn Drive,
Gloucester, MA 01930–2298.
FOR FURTHER INFORMATION CONTACT: Eric
Jay Dolin, Fishery Policy Analyst, 978–
281–9259, e-mail at
eric.dolin@noaa.gov, fax at 978–281–
9135.
DATES:
SUPPLEMENTARY INFORMATION:
Background
Proposed 2007–2009 specifications
were published on January 10, 2007 (72
FR 1206 ), with public comment
accepted through February 9, 2007.
These final specifications are
unchanged from those that were
proposed. A complete discussion of the
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development of the specifications
appears in the preamble to the proposed
rule and is not repeated here.
2007–2009 Final Initial Specifications
The following specifications are
established by this action: Allowable
biological catch (ABC), optimum yield
(OY), domestic annual harvest (DAH),
domestic annual processing (DAP), total
foreign processing (JVPt), joint venture
processing (JVP), internal waters
processing (IWP), U.S. at-sea processing
(USAP), border transfer (BT), total
allowable level of foreign fishing
(TALFF), and total allowable catch
(TAC) for each management area and
subarea.
TABLE 1. SPECIFICATIONS AND AREA TACS FOR THE 2007–2009 ATLANTIC HERRING FISHERY
Specification
2007 Allocation (mt)
2008–2009 Allocation (mt)
ABC
194,000
194,000
OY
145,000
145,000
DAH
145,000
145,000
DAP
141,000
141,000
JVPt
0
0
JVP
0
0
IWP
0
0
USAP
20,000
(Areas 2 and 3 only)
20,000
(Areas 2 and 3 only)
BT
4,000
4,000
TALFF
0
0
Reserve
0
0
TAC - Area 1A
50,000
[48,500 fishery; 1,500 RSA]
(January 1 - May 31, landings cannot exceed 5,000)
45,000
[43,650 fishery; 1,350 RSA]
(January 1 - May 31, landings cannot exceed 5,000)
TAC - Area 1B
10,000
[9,700 fishery; 300 RSA]
10,000
[9,700 fishery; 300 RSA]
TAC - Area 2
30,000
[29,100 fishery; 900 RSA]
(No Reserve)
30,000
[29,100 fishery; 900 RSA]
(No Reserve)
TAC - Area 3
55,000
[53,350 fishery; 1,650 RSA]
60,000
[58,200 fishery; 1,800 RSA]
Research Set Aside
3 percent from each area TAC
(2008 and 2009 FY only)
3 percent from each area TAC
(2008 and 2009 FY only)
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Comments and Responses
There were 460 comments received.
Commenters included the American
Pelagic Association; Cape Seafoods;
Center for Oceanic Research and
Education; Conservation Law
Foundation; Garden State Seafood
Association; Bumblebee Seafoods/
Stinson Seafood; Maine Department of
Marine Resources; Mid-Atlantic Fishery
Management Council; Northern Pelagic
Group, LLC; Ocean Conservancy; and
451 individuals and vessel owners.
Comment 1: Three organizations and
448 individuals support the proposed
rule, especially NMFS’s decision to
reduce the Area 1A TAC to 45,000 mt
in 2008 and 2009.
Response: This action is unchanged
from the proposed rule.
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Comment 2: Two organizations and
three vessel owners opposed the
Council’s recommendation to reduce the
Area 1A TAC to 50,000 mt for 2007–
2009, and strongly opposed NMFS’s
further reduction of the Area 1A TAC to
45,000 mt for 2008 and 2009. They
argue that the Council’s
recommendation was unnecessarily
restrictive, in light of the stock’s status.
They further argue that NMFS should
not have relied on the Plan
Development Team’s (PDT’s) risk
assessment in making its decision to
further reduce the Area 1A TAC to
45,000 mt because it was not peerreviewed, and was overly conservative.
They disagreed that the Councils’ and
NMFS’s concern about the retrospective
pattern in the stock assessment is an
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appropriate reason to reduce the Area
1A TAC. They argued that the 29,000–
mt buffer between ABC and OY was
intended to account for the retrospective
pattern and that it is, therefore,
scientifically inappropriate to further
reduce the Area 1A TAC. The
commenters argue that the Council’s
specifications document pointed out
that trawl survey results are highly
variable, and that no trends are apparent
from the most recent years of the survey
across all strata. The commenters state
that encounter rates are increasing,
rather than declining, and a broader size
distribution is evident; and that both of
these trends indicate a healthy resource.
One organization stated that it is
misleading for NMFS to state that there
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is considerable overlap between the
inshore stock component and Area 1A.
One organization supported the
reduction of the Area 1A TAC to 50,000
mt, but not to 45,000 mt in 2008 and
2009. They argue that the retrospective
pattern described by the Transboundary
Resource Assessment Committee
(TRAC) applies to the stock as a whole,
and not individual stock components,
and that the 29,000–mt buffer between
ABC and OY addresses the issue. They
stated that the reduction in the Area 1A
TAC to 45,000 mt and commensurate
increase in the Area 3 TAC does not
account for the retrospective pattern,
because it maintains OY at the same
level. They also argued that only the
NMFS fall survey shows a decline in
abundance and biomass, and the other
surveys are either increasing or variable
and stable. They noted that the PDT
suggested that encounter rates may be a
better indicator of stock status for
herring, and that the Northeast Fisheries
Science Center (NEFSC) fall surveys are
not showing a decline in the encounter
rates, and the Massachusetts inshore
survey is showing an increase in
encounter rates.
One organization opposed the
reduction of Area 1A TAC, but provided
no additional rationale. One vessel
owner argued that the industry was not
allowed to participate in the Advisory
Panel’s decisionmaking during the
specifications-setting process.
Response: The herring stock is in
good shape. However, both the Council
and NMFS agree that, while the overall
stock is healthy, there is a clear need to
be precautionary with the inshore
component of the stock. This is directly
related to the establishment of the Area
1A TAC because, contrary to some
comments, there is substantial overlap
between the inshore stock component
and Area 1A. The inshore component, at
different times of year, is distributed
throughout Areas 1A, 1B, and 2. Based
on the stock mixing ratios employed in
the specifications document (and in the
FMP), it is reasonable to state that there
is a considerable amount of overlap
between the inshore stock component
and Area 1A. The specifications
document estimates that, in the
summer, 50 percent of the catch from
Area 1A comes from the inshore
component. In the winter, 100 percent
of the catch in Area 1A, and 20 percent
of the catch in Area 2, is assumed to
come from the inshore component of the
resource. Removals from Area 1B are
assumed to be composed of 30 percent
of the inshore component at all times of
the year.
Several aspects of the specifications
analyses provided a strong basis for
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NMFS to enact the Area 1A TACs
specified in this action. Three elements
in particular contributed to NMFS’s
determination that the 2008–2009 TACs
should be set lower than recommended
by the Council.
The Council’s Scientific and
Statistical Committee (SSC) met in 2003
to consider the status of the herring
stock and found, among other things,
that ‘‘no severe declines in the stock
complex should be expected by
maintaining current levels of catches
over the short-term; however, the
current concentration of harvest in the
inshore Gulf of Maine is of concern and
may be excessive.’’ Thus, NMFS
concluded that the issue is not whether
there is a need for more caution when
establishing the Area 1A TAC, but
rather, how much caution is necessary.
Both the Council and NMFS agreed
that the available data and concerns
warranted a significant reduction in the
Area 1A TAC over the next 3 years.
NMFS, however, concluded that the
Council’s proposal, to set the Area 1A
TAC at 50,000 mt, did not go far enough
to protect the stock in Area 1A.
NMFS also concluded that the
retrospective pattern in the stock
assessment, which overestimates
biomass and underestimates fishing
mortality in the terminal year of the
assessment, argues for caution. NMFS
concluded that for the stock as a whole,
the buffer of 29,000 mt between ABC
(maximum OY) and OY specified in this
action would help ensure that adequate
spawning stock biomass (SSB) is
available to produce strong recruitment
in the future. However, the retrospective
pattern indicates that, as more data are
collected and analyzed, the stock,
including the inshore stock component,
will be found to be not as robust as
current data imply.
Finally, the PDT’s risk assessment
provides a useful tool for evaluating
TAC alternatives. The risk assessment is
a tool that the Council asked the PDT to
provide, and it was presented and
debated by the PDT members, the
Herring Advisory Panel (AP), and the
Herring Committee, as well as the
Council. According to the risk
assessment, setting the Area 1A TAC at
45,000 mt for 2008–2009 will provide a
slightly improved chance of producing
exploitation rates that are more
consistent with Fmsy for the stock
component, within a range of realistic
stock mixing ratios. Therefore, NMFS
finds that the SSC advice, the
retrospective pattern in the stock
assessment, and the conclusions of the
PDT’s risk assessment combine to make
a sound case for specifying the Area 1A
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TAC at 45,000 mt in fishing years 2008
and 2009.
The commenters correctly
characterize the variability of the trawl
survey data and encounter rates. While
NMFS acknowledges these points, it
does not conclude that they overcome
the concerns noted above. More
specifically, although some of the
encounter rates do not indicate a
decline in stock status, they are just one
of the indicators that the Council and
NMFS needs to rely on in determining
the appropriate levels for the various
TACs. As mentioned above, taken
together, the SSCs advice, the
significant retrospective pattern in the
stock assessment, and the PDT’s risk
assessment, even in the face of some
positive or stable encounter rates, justify
the precautionary approach being taken
in this rule.
NMFS does not share the
commenters’ concerns about the use of
the PDT’s risk assessment. PDTs are
established by the Council specifically
to offer technical advice that will assist
in making sound fishery management
decisions. The current process for
obtaining the PDT’s advice does not
include an additional formal peer
review of that advice. A certain amount
of informal peer review is built into the
PDT process by virtue of its membership
and the debates that take place at PDT
meetings, the Council’s committee
meetings, and Council meetings. An
additional layer of informal peer review
takes place within NMFS, when the
specifications package, including the
PDT’s products, are reviewed by NMFS
staff.
The perception that the industry was
not allowed to participate in the AP’s
deliberations is not accurate. Not only is
the AP comprised of industry members,
but all of its meetings were public
meetings, for which public notice was
provided. At those meetings a variety of
industry members contributed their
thoughts and ideas to the process,
although not all of their suggestions
were ultimately adopted.
Comment 3: Two organizations
argued that the reduction of the Area 1A
TAC to 45,000 mt is not justified. They
also argued that the PDT analysis was
presented to the Council at the last
minute and that participants in the
fishery did not have adequate
opportunity to review and comment on
it. One commenter argued that the use
of this new analysis appears contrary to
the recent Congressional reauthorization
of the Magnuson-Stevens Fishery
Conservation and Management Act
(Magnuson-Stevens Act), which
specifies in section 302(g) that, ‘‘The
Secretary and each Council may
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establish a peer review process for that
Council for scientific information used
to advise the Council about the
conservation and management of the
fishery.’’ Finally, this commenter argued
that the assumption in the specifications
that the New Brunswick (NB) weir
fishery will catch 20,000 mt annually is
an overestimate and, therefore, it serves
to provide an additional level of caution
in the specifications.
Response: The justification for setting
the Area 1A TAC at 45,000 mt and the
concerns about the PDT’s risk
assessment are addressed in the
response to Comment 2. NMFS notes
that the Council process provided
several opportunities for public
comment, including comment on the
risk assessment.
The new Magnuson-Stevens Act
requirement is not retroactively
applicable to the process the Council
followed to develop these herring
specifications.
The Council adopted the estimate that
the NB weir fishery will land 20,000 mt
annually after public debate. Though in
recent years landings by this fishery
have not attained 20,000 mt, the Council
and NMFS concluded it is a reasonable
estimate. Historical catches in the NB
weir fishery were much higher than
those in recent years, and exceeded
20,000 mt in many years prior to 1995.
Landings of herring in the NB weir
fishery average 22,475 mt for 1978–
2005, despite the fact that the 2005
landings are currently estimated to have
been about 13,000 mt.
Comment 4: Five vessel owners
pointed out that there is no stock
assessment for the inshore component
and, therefore, the target and threshold
fishing mortality rates for the inshore
stock component remain uncertain.
Because of this, the owners argue that
reducing the Area 1A TAC based on a
concern that the Council’s
recommendations for 2008 and 2009
would be only marginally successful at
producing an exploitation rate
consistent with Fmsy is not justified,
because the Fmsy for the inshore
component remains uncertain.
Furthermore, these owners pointed out
that, although the TRAC assessment
estimated that the inshore component of
the stock represents 18 percent of the
total stock biomass, the TRAC
assessment does not provide guidance
on the TAC allocations by management
area or the mixing rates between stock
components. The owners find the use of
the 18 percent value to be problematic,
and cast doubt on the usefulness of the
PDT’s risk assessment because it is not
peer-reviewed. The risk assessment
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should not, they contend, be used as a
justification for draconian cuts.
Response: The commenters are correct
that the stock assessment does not
provide specific fishing mortality target
and threshold rates for the inshore stock
component or the specification of
management area TACs. However,
NMFS concluded that it is appropriate
to use the risk assessment and the TRAC
estimate that the inshore stock
component represents 18 percent of the
total biomass, for reasons outlined in
detail in the response to Comment 2.
The stock mixing ratios used in the risk
assessment are, as the specifications
document points out, supported by the
best available scientific information.
Comment 5: Five organizations argued
that the proposed reallocation of 5,000
mt from Area 1A to Area 3 should,
instead, be a reallocation of the same
amount into a reserve for Area 2. The
rationale offered is that a higher
percentage of the Area 2 TAC has been
taken in recent years than of the Area
3 TAC. The establishment of such a
reserve would, the commenters argue,
increase the amount of herring available
to the Atlantic mackerel fishery, which
has an incidental catch of herring. This
would reduce the likelihood of a closure
of the herring fishery in Area 2. The
commenters believe that a herring
closure would de facto close the
mackerel fishery in that area because
vessels would not fish in the area for
mackerel if they could not also retain
more than 2,000 lb (907.2 kg) of herring.
Response: There are two reasons for
transferring the 5,000 mt from Area 1A
to Area 3. First, since Area 3 fish are
assumed to come entirely from the
offshore component of the stock, the
addition of 5,000 mt to that Area’s TAC
will not impact the status of the inshore
component. Second, this reallocation
will increase opportunities for the fleet
to fish for herring in Area 3 and,
therefore, support one of the FMP’s
goals, which is to provide for the
orderly development of the offshore
herring fishery. In contrast, because of
mixing of the subcomponents of the
stock, a shift of 5,000 mt from Area 1A
to Area 2 would still allow the fishery
to harvest from the inshore stock
component.
On a practical level, the Area 2 TAC
has never been fully harvested. In 2006,
roughly 22,000 mt of herring was landed
from this area, while in the 4 prior
years, landings from the area ranged
from 11,000 mt to 16,000 mt. In light of
this history, the 30,000 mt allocated to
Area 2 would appear unlikely to
constrain the mackerel fishery. The
Council has the option of reviewing
information relating to the herring stock
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and fishery in 2007 and revising the
Area 2 TAC for 2008–2009, if warranted.
Comment 6: Two organizations urged
that a portion of the DAH be set-aside
for use in value-added food grade
products, and that such an allocation
would be consistent with the allocation
of 20,000 mt for USAP. These
commenters also urged NMFS to
establish three different fishing seasons
within Area 1A, and to apportion the
TAC among those seasons to extend the
fishing season in Area 1A, achieve OY,
and more effectively protect prespawning herring.
Response: These suggestions would
require amendment of the Herring FMP,
which defines the allocations that must
be recommended by the Council and
enacted by NMFS, and are therefore
outside the scope, purpose, and
authority of this action. Such changes
may be pursued through the Council
process.
Comment 7: Two organizations
argued that the Council’s decision to
review the new survey data during 2007
and determine whether adjustments
should be made to the specifications for
the 2008 and 2009 fishing years was
sufficiently precautionary and should be
allowed to proceed. One organization
believed that NMFS’s revision of the
allocations for 2008–2009 precluded the
Council from conducting a review of the
fishery during the 3–year specification
period.
Response: NMFS’s decision to reduce
the Area 1A TAC to 45,000 mt for the
2008 and 2009 fishing years has no
bearing on the review process that the
Council stated that it plans to conduct
during 2007. That review is expected to
take place, and the Council is at liberty
to recommend changes to the
specifications for 2008 and/or 2009
based on its review, if warranted.
Comment 8: Five vessel owners
supported the implementation of the
status quo specifications for the herring
fishery, which would set OY at 150,000
mt, the Area 1A TAC at 60,000 mt, and
the Area 3 TAC at 50,000 mt. They
argue that the recent landings levels of
around 100,000 mt are sustainable. They
note that the TRAC report supports this
view, and that the PDT analysis
indicates that all of the alternatives,
including the status quo, are projected
to result in removals of the inshore
component that are less than the
historical (1995–2006) removals within
a reasonable range of stock mixing
assumptions.
Response: The commenters are correct
in noting that the TRAC concluded that
removals at current levels (around
100,000 mt per year for the past 15
years) are sustainable. They are also
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correct that the PDT’s risk assessment
indicated that setting the TACs at the
status quo level was projected to result
in removals from the inshore stock
component that are less than historical
removals for the period 1995–2005,
during the winter (January-March;
August-December). However, the PDT’s
risk assessment was not as clear cut for
the summer period (April-July), where it
showed that the status quo TACs would
generate removals that would be at or
below historical removals in about 50
percent of the possible scenarios. Both
the Council’s recommended TACs and
the TACs established by this action
would be more risk-averse than the
status quo during the summer period,
when a large amount of the Area 1A
catch is taken.
The commenters failed to note that
there was a second part to the PDT’s risk
assessment, which evaluated the
success of proposed TAC alternatives in
achieving an exploitation rate that
equates to Fmsy for the herring stock. As
noted in the response to Comment 2,
this aspect of the risk assessment was
one of the reasons that both the Council
and NMFS concluded that it was
appropriate to make a significant
reduction in the Area 1A TAC to reduce
the risk of overfishing the inshore stock
component.
Comment 9: One organization argued
that, based on the TRAC results and
reasonable assumptions about stock
component mixing rates, the Area 1A
TAC should be set between 35,000–
42,000 mt. Furthermore, this
organization does not support the
addition of 5,000 mt to the Area 3 TAC,
and argues that, at most, the Area 3 TAC
should be 55,000 mt. The commenter
argues that, because the natural
mortality rate used by the TRAC in its
assessment model is not accurate and
might significantly underestimate
natural mortality, NMFS has not
accurately estimated the amount of
herring that can be safely removed from
the ecosystem and that, as a result,
NMFS should be more precautionary in
setting the herring specifications.
Response: The PDT stated that if it
may be possible to apply a fishing
mortality rate to an average biomass for
the inshore stock component (assuming
that it comprises 18 percent of total
biomass), and estimate a TAC
specifically for the inshore stock
component. Using this approach would
likely result in a TAC for the inshore
stock component of about 35,000 mt 42,000 mt. However, the PDT also stated
that a TAC for the inshore stock
component does not equate to a TAC for
Area 1A, as fish from both the inshore
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and offshore component are caught in
Areas 1A, 1B, and 2.
Regarding the commenter’s
contention that the natural mortality
rate used in the TRAC assessment is not
accurate, the TRAC investigated values
for natural mortality other than 0.2, but
deemed that 0.2 was the appropriate
value to use in the stock assessment.
The peer-reviewed TRAC results
constitute the best available scientific
information on this point.
NMFS notes that Fmsy for the stock
was estimated at 0.31 by the TRAC. The
analysis of the stockwide F associated
with the specifications estimates F’s of
0.18 in 2007; 0.197 in 2008, and 0.221
in 2009. NMFS concludes that these
fishing mortality estimates are
sufficiently precautionary.
Comment 10: Five vessel owners
argued that the perceived declines in
the inshore component, based on the
incorporation of recent data (2004 and
2005) from the NMFS trawl survey,
appears to be a rush to judgment. They
pointed out that, in 2006, herring
fishermen reported very high inshore
biomass and that, based on a personal
communication with NEFSC staff, the
fall 2006 survey results indicate a
rebound to previous levels.
Response: The PDT noted the impact
that recent data has on overall trends for
the inshore component; however it also
placed that data within its proper
context, stating that, ‘‘While data
specific to the inshore component of the
stock is limited and the Herring PDT
cannot make a status determination
based on bottom trawl indices alone, a
change in the direction of the trend line
is an important consideration.’’ The
Council’s 2007 review will consider any
upated survey data and, if the results
indicate a change in the apparent trend
of recent years, then it could result in
recommendations for TAC adjustments
in 2008–2009. While NMFS took recent
trawl survey information into account in
taking this action, there were several
factors that led NMFS to specify the
Area 1A TAC at 45,000 mt for 2008–
2009, as discussed in the response to
Comment 2.
Comment 11: Five vessel owners
argued that the 10,000–15,000 mt
reduction of the Area 1A TAC will have
greater economic impacts than the
revenue loss estimates of $136,350–
204,500 per vessel for purse seine
vessels. They contend that it is incorrect
to assume that the reduced catch in
Area 1A can be made up from Area 3.
They explain that vessel size and
weather make it difficult for their
vessels to work offshore and make up
for reduced landings from Area 1A.
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Response: The analysis of the
economic impacts of the proposed TACs
takes into account the same points made
by the commenter. The specific pervessel revenue impacts cited by the
commenter are part of the analysis of
revenue impacts on vessels that have
harvested herring from Area 1A in the
past, and are likely to qualify for the
limited access permit established by
Amendment 1. The analysis presumes
that these vessels will continue to
harvest the same proportion of the Area
1A TAC as in the past. The analysis
notes that there are several things that
could affect this assumption, notably
that the reduced TAC may create an
incentive for vessel owners to compete
more aggressively for the reduced Area
1A TAC, thus altering the proportion of
fish available to past participants. The
analysis also notes that, while there are
opportunities to harvest fish from other
management areas to compensate for the
reduction in Area 1A, this may not be
possible for all vessels. It notes that
there are a number of reasons it may not
be possible for all vessels to fish in other
areas, particularly offshore Areas 2 and
3, because the size of some vessels
creates safety concerns, and because
there are higher operating costs
associated with longer trips, notably the
costs associated with additional
steaming time and associated fuel costs.
Comment 12: One organization argued
that, because of the mixing between
offshore and inshore components during
the spring, only the fall surveys should
be considered as an indicator of the
status of the inshore stock component.
It also argued that a number of the
survey results, as well as observed
encounter rates, indicate that the health
of the stock is not in decline.
Response: Overall, the herring stock is
in good shape, but for reasons outlined
in the response to Comment 2 there are
concerns about the inshore stock
component that resulted in the
reduction of the Area 1A TAC.
Classification
This action is authorized by 50 CFR
part 648 and has been determined to be
not significant for purposes of Executive
Order 12866.
A FRFA was prepared. The FRFA
incorporates the IRFA, a summary of the
signficant issues raised by the public
comments in response to the IRFA,
NMFS responses to those comments,
and a summary of the analyses
completed to support the action. A copy
of the analyses is available from NMFS
(see ADDRESSES).
A description of the reasons for this
action, the objectives of this action, and
the legal basis for this final rule is found
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in the preambles to the proposed rule
and this final rule and is not repeated
here.
Statement of Need for this Action
The purpose of this action is to
establish specifications to conserve and
manage the herring resource for the
period 2007–2009, as required by the
FMP.
A Summary of the Significant Issues
Raised by the Public Comments in
Response to the IRFA, a Summary of the
Assessment of the Agency of Such
Issues, and a Statement of Any Changes
Made in the Proposed Rule as a Result
of Such Comments
NMFS received 460 comments on the
proposed specifications. Only one
comment was specific to the IRFA.
Comment 12 outlines concerns
expressed by five vessel owners that the
analysis of the Area 1A TACs
underestimated the economic impacts
they would experience due to the
reductions in the allocation for the area.
NMFS’ assessment of the issues raised
by this comment is contained in the
preamble and not repeated here. The
comment did not result in any changes
to the Area 1A TAC, which was reduced
for biological reasons.
Description and Estimate of Number of
Small Entities to Which the Rule Will
Apply
During the 2005 fishing year, 143
vessels landed herring, 33 of which
averaged more than 2,000 lb ( 907 kg)
of herring per trip. The Small Business
Administration’s size standard for small
commercial fishing entities is $4 million
in gross sales. Thus, all the entities
participating in this fishery are
considered small entities, as defined in
section 601 of the RFA. Therefore, there
are no disproportionate economic
impacts between large and small
entities.
Description of Projected Reporting,
Recordkeeping, and Other Compliance
Requirements
cprice-sewell on PROD1PC66 with RULES
This action does not contain any new
collection-of-information, reporting,
recordkeeping, or other compliance
requirements.
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13:19 Apr 09, 2007
Jkt 211001
Description of the Steps the Agency Has
Taken to Minimize the Significant
Economic Impact on Small Entities
Consistent with the Stated Objective of
Applicable Statutes, including a
Statement of the Factual, Policy, and
Legal Reasons for Selecting the
Alternative Adopted in the Final Rule
and Why Each of the Other Significant
Alternatives to the Rule Considered by
the Agency which Affect the Impact on
Small Entities was Rejected
The economic impacts of this action
were assessed by the Council and NMFS
in an analysis that compares the
alternatives considered to the herring
landings made in 2005, the most recent
year for which complete data are
available. From a fishery-wide
perspective, these specifications are not
expected to produce a negative
economic impact to vessels prosecuting
the fishery because it allows for
landings levels that are significantly
higher than the landings in recent years.
The 2007–2009 specifications should
allow for incremental growth in the
industry, while appropriately
addressing biological concerns.
However, because of the allocation of
the management area TACs, and the
reduction in the Area 1A TAC in
particular, these specifications could
have a negative impact on various
industry participants, despite the fact
that overall landings levels could be
higher than in recent years.
The specification of OY and DAH is
145,000 mt for 2007–2009. While higher
levels of OY were considered (150,000
mt and 170,000 mt) the OY of 145,000
mt will allow an annual increase of up
to 51,610 mt in herring landings
compared to the 93,390 mt landed in
2005. This will generate $10.4 million
in revenues, based on an average price
(in 2005) of $202/mt. Therefore, there
are no negative economic impacts
associated with the specification of OY
in this action. Individual vessels could
increase their revenues under the
proposed 2007–2009 specifications,
depending on the number of vessels
participating in the fishery, which will
become a limited access fishery with the
implementation of Amendment 1 to the
FMP on June 1, 2007.
Several other specifications
established by this action would also
allow an increase in revenue to industry
participants when compared to the 2005
landings. These include DAH and DAP,
which are specified at 145,000 mt and
141,000 mt, respectively; USAP, which
is specified at 20,000 mt; the Area 1B
TAC, which is specified at 10,000 mt;
the Area 2 TAC, which is specified at
30,000 mt; and the Area 3 TAC, which
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Fmt 4700
Sfmt 4700
is specified at 55,000 mt in 2007 and
60,000 mt in 2008–2009. In each
instance, there are no negative economic
impacts associated with these
specifications because they would allow
industry participants to harvest and/or
process more herring than in 2005.
There are no potential economic
impacts associated with the allocation
for JVPt of zero, because it is unchanged
from 2005.
The only specification that could
constrain the industry when compared
to landings and revenue in 2005 is
reduction of the Area 1A TAC to 50,000
mt in 2007, and 45,000 mt in 2008 and
2009. The impacts of these reductions
were analyzed for the purse seine fleet,
the single midwater trawl fleet, and the
paired midwater trawl fleet.
In 2005, the currently active purse
seine fleet caught 27 percent of the Area
1A TAC. With a 10,000–15,000–mt
reduction in the Area 1A TAC, if the
proportion of the herring catch by the
purse seine fleet remains the same and
the decrease in the Area 1A TAC cannot
be made up from fishing in other areas,
there would be a 2,700–mt loss in catch
under this action in 2007, and a 4,050–
mt loss in catch in 2008 and 2009. Using
the 2005 average price of herring of
$202 per metric ton, this loss in catch
would be worth $545,400 and $818,000,
respectively, across the sector (there are
four vessels in the currently active purse
seine fleet). To make up for such a loss,
these vessels would have to either
increase their proportion of the herring
catch in Area 1A relative to midwater
trawlers, or move to other areas. There
were no landings from Area 3 by these
purse seine vessels in 2005, likely
reflecting the fact that the vessels are too
small to fish in these offshore areas.
Moving offshore would also entail
additional operating costs because the
trips would be longer.
The impact of the 10,000–15,000–mt
decrease in the Area 1A TAC on the
single midwater trawl fleet is difficult to
predict, because the Purse Seine/Fixed
Gear (PS/FG) only area established by
Amendment 1 will eliminate single
midwater trawl vessels from Area 1A
during the most productive part of the
Area 1A fishery (June through
September). The establishment of a PS/
FG only area might intensify the race to
fish in Area 1A, as midwater trawl
vessels (single and paired) may try to
catch more fish from the area prior to
the closure to trawling on June 1.
If herring are plentiful in Area 1A
during the spring (Area 1A catches
increase in May, historically), the single
midwater trawlers may be able to
maintain their historical proportion of
the Area 1A TAC. However, it is likely
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that purse seine vessels and midwater
pair trawl vessels would also participate
in the pre-June race in order to keep
their landings on par with previous
years. In addition, single midwater trawl
vessels might convert to purse seine
gear in order to fish in Area 1A in the
summer.
In 2005, the currently active single
midwater trawl fleet caught 18 percent
of the Area 1A TAC. If the proportion
of the herring catch by the single
midwater trawl fleet remains the same,
and the decrease in the Area 1A TAC
cannot be made up from fishing in other
areas, there would be a 1,800–mt loss in
catch under this action during 2007, and
a 2,700–mt loss in catch in 2008 and
2009. Using the 2005 average price of
herring of $202 per metric ton, this loss
in catch would be worth $363,600 and
$545,400, respectively, across the sector
(there are four vessels that were active
in Area 1A from 2003–2005 in the single
midwater trawl fleet). To make up for
such a loss, the single midwater trawl
vessels would have to either increase
their proportion of the herring catch in
Area 1A relative to purse seine vessels,
or move to other areas. Moving to
offshore areas may be problematic for
two of the four single midwater trawl
vessels, since these two are relatively
smaller vessels and landed herring only
from Area 1A during 2003 through
2005. The other two vessels are
somewhat larger and have Area 3 catch
history, so their loss of Area 1A catch
may be mitigated by their ability to fish
in Area 3. If the single midwater trawl
vessels make up their catch in Areas 2
and 3, the vessel operating cost will
increase because the trips will be longer.
With decreases in the Area 1A TAC of
10,000 mt to 15,000 mt under this
action, the impact on the midwater pair
trawl fleet could also be large. It is
difficult to predict what the impact will
be on the midwater pair trawl fleet,
because these vessels will also be
excluded from Area 1A for the period
June-September due to the PS/FG only
measure. In 2005, the currently active
pair trawl fleet caught 55 percent of the
Area 1A TAC. If the proportion of the
herring catch by the pair trawl fleet
remains the same and the decrease in
the Area 1A TAC cannot be made up
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13:19 Apr 09, 2007
Jkt 211001
from fishing in other areas, there would
be a 5,500–mt loss in catch under this
action in 2007, and a 8,250–mt loss in
2008 and 2009. Using the 2005 average
price of herring of $202 per metric ton,
this catch is worth $1,111,000 and
$1,666,500 respectively, across the
sector (there are 12 vessels in the pair
trawl fleet that were active from 2003–
2005). To make up for such a loss, pair
trawl vessels would have to either
increase their proportion of the herring
catch in Area 1A or move to other areas.
All pair trawl vessels have Area 3 catch
history, so their loss of Area 1A catch
may be mitigated by their ability to fish
in Area 3. If the pair trawl vessels make
up their catch in Areas 2 and 3, the
vessel operating cost will increase
because the trips would be longer.
The 10,000–mt to 15,000–mt
reduction in TAC in Area 1A may cause
participants using all 3 gear types to
increase their fishing activity in Area
1B. The Area 1B TAC has not been
reached every year, and only 60 percent
was harvested in 2005. Since Area 1B is
farther from shore than Area 1A, vessel
operating costs would increase because
trips would be longer. Harvesting in
Area 1B will only provide limited relief
for vessels impacted by the reduction in
the Area 1A TAC since the TAC is
limited to 10,000 mt.
There were seven alternatives
considered. Three of the alternatives
would have set the Area 1A TAC at
60,000 mt. They were rejected because
the biological concerns about the
inshore herring stock component
require a significant reduction in
harvest within Area 1A. More
specifically, NMFS concluded that the
SSC’s advice, the retrospective pattern
in the stock assessment, and the
conclusions of the PDT’s risk
assessment combine to make a sound
case for being precautionary about
protecting the inshore component and
for specifying the Area 1A TAC at
45,000 mt.
One alternative would have set the
Area 1A TAC at 50,000 mt for all three
years. This was rejected for the reasons
cited above; namely, that the SSC’s
advice, the retrospective pattern in the
stock assessment, and the conclusions
of the PDT’s risk assessment combine to
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17813
make a sound case for being
precautionary about protecting the
inshore component and for specifying
the Area 1A TAC at 45,000 mt.
Two of the alternatives would have
reduced the Area 1A TAC to 45,000 mt
for all three years. These were rejected
because NMFS believed that it is
sufficient to achieve biological
objectives to implement the 45,000 mt
TAC for 2008–2009, and establish the
2007 TAC at 50,000 mt, consistent with
action taken by the states under the
Atlantic States Marine Fisheries
Commission’s Interstate Fisheries
Management Plan for Atlantic Sea
Herring. The preferred alternative was
selected because the SSC’s advice, the
retrospective pattern in the stock
assessment, and the conclusions of the
PDT’s risk assessment combine to make
a sound case for specifying the Area 1A
TAC at 45,000 mt in fishing years 2008
and 2009.
Small Entity Compliance Guide
Section 212 of the Small Business
Regulatory Enforcement Fairness Act of
1996 states that, for each rule, or group
of related rules, for which an agency is
required to prepare a FRFA, the agency
shall publish one or more guides to
assist small entities in complying with
the rule and shall designate such
publications as ‘‘small entity
compliance guides.’’ The agency shall
explain the actions a small entity is
required to take to comply with a rule
or group of rules. As part of this
rulemaking process, a small entity
compliance guide will be sent to all
holders of permits issued for the herring
fishery. In addition, copies of this final
rule and guide (i.e., permit holder letter)
are available from the Regional
Administrator (see ADDRESSES) and may
be found at the following web site:
https://www.nero.noaa.gov.
Authority: 16 U.S.C. 1801 et seq.
Dated: April 2, 2007.
John Oliver,
Deputy Assistant Administrator for
Operations, National Marine Fisheries
Service.
[FR Doc. E7–6648 Filed 4–9–07; 8:45 am]
BILLING CODE 3510–22–S
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Agencies
[Federal Register Volume 72, Number 68 (Tuesday, April 10, 2007)]
[Rules and Regulations]
[Pages 17807-17813]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-6648]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 648
[Docket No. 061228342-7068-02; I.D. 122206A]
RIN 0648-AT66
Fisheries of the Northeastern United States; Atlantic Herring
Fishery; 2007-2009 Specifications
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS announces final specifications for the 2007-2009 fishing
years for the Atlantic herring (herring) fishery. The intent of this
final rule is to conserve and manage the herring resource and provide
for a sustainable fishery.
DATES: Effective May 10, 2007, through December 31, 2009.
ADDRESSES: Copies of supporting documents, including the Environmental
Assessment, Regulatory Impact Review, Initial Regulatory Flexibility
Analysis (EA/RIR/IRFA), and Essential Fish Habitat Assessment are
available from Paul J. Howard, Executive Director, New England Fishery
Management Council, 50 Water Street, Mill 2, Newburyport, MA 01950. The
EA/RIR/IRFA is also accessible via the Internet at https://www.nero.gov.
NMFS prepared a Final Final Regulatory Flexibility Analysis (FRFA), a
summary of which is contained in the Classification section of the
preamble of this final rule. Copies of the FRFA and the Small Entity
Compliance Guide are available from Patricia A. Kurkul, Regional
Administrator, Northeast Region, National Marine Fisheries Service, One
Blackburn Drive, Gloucester, MA 01930-2298.
FOR FURTHER INFORMATION CONTACT: Eric Jay Dolin, Fishery Policy
Analyst, 978-281-9259, e-mail at eric.dolin@noaa.gov, fax at 978-281-
9135.
SUPPLEMENTARY INFORMATION:
Background
Proposed 2007-2009 specifications were published on January 10,
2007 (72 FR 1206 ), with public comment accepted through February 9,
2007. These final specifications are unchanged from those that were
proposed. A complete discussion of the
[[Page 17808]]
development of the specifications appears in the preamble to the
proposed rule and is not repeated here.
2007-2009 Final Initial Specifications
The following specifications are established by this action:
Allowable biological catch (ABC), optimum yield (OY), domestic annual
harvest (DAH), domestic annual processing (DAP), total foreign
processing (JVPt), joint venture processing (JVP), internal waters
processing (IWP), U.S. at-sea processing (USAP), border transfer (BT),
total allowable level of foreign fishing (TALFF), and total allowable
catch (TAC) for each management area and subarea.
Table 1. Specifications and Area TACs for the 2007-2009 Atlantic Herring Fishery
----------------------------------------------------------------------------------------------------------------
Specification 2007 Allocation (mt) 2008-2009 Allocation (mt)
----------------------------------------------------------------------------------------------------------------
ABC 194,000 194,000
----------------------------------------------------------------------------------------------------------------
OY 145,000 145,000
----------------------------------------------------------------------------------------------------------------
DAH 145,000 145,000
----------------------------------------------------------------------------------------------------------------
DAP 141,000 141,000
----------------------------------------------------------------------------------------------------------------
JVPt 0 0
----------------------------------------------------------------------------------------------------------------
JVP 0 0
----------------------------------------------------------------------------------------------------------------
IWP 0 0
----------------------------------------------------------------------------------------------------------------
USAP 20,000 20,000
(Areas 2 and 3 only) (Areas 2 and 3 only)
----------------------------------------------------------------------------------------------------------------
BT 4,000 4,000
----------------------------------------------------------------------------------------------------------------
TALFF 0 0
----------------------------------------------------------------------------------------------------------------
Reserve 0 0
----------------------------------------------------------------------------------------------------------------
TAC - Area 1A 50,000 45,000
[48,500 fishery; [43,650 fishery; 1,350 RSA]
1,500 RSA] (January 1 - May 31, landings cannot exceed 5,000)
(January 1 - May 31,
landings cannot
exceed 5,000)
----------------------------------------------------------------------------------------------------------------
TAC - Area 1B 10,000 10,000
[9,700 fishery; 300 [9,700 fishery; 300 RSA]
RSA]
----------------------------------------------------------------------------------------------------------------
TAC - Area 2 30,000 30,000
[29,100 fishery; 900 [29,100 fishery; 900 RSA]
RSA] (No Reserve)
(No Reserve)
----------------------------------------------------------------------------------------------------------------
TAC - Area 3 55,000 60,000
[53,350 fishery; [58,200 fishery; 1,800 RSA]
1,650 RSA]
----------------------------------------------------------------------------------------------------------------
Research Set Aside 3 percent from each 3 percent from each area TAC
area TAC (2008 and 2009 FY only)
(2008 and 2009 FY
only)
----------------------------------------------------------------------------------------------------------------
Comments and Responses
There were 460 comments received. Commenters included the American
Pelagic Association; Cape Seafoods; Center for Oceanic Research and
Education; Conservation Law Foundation; Garden State Seafood
Association; Bumblebee Seafoods/Stinson Seafood; Maine Department of
Marine Resources; Mid-Atlantic Fishery Management Council; Northern
Pelagic Group, LLC; Ocean Conservancy; and 451 individuals and vessel
owners.
Comment 1: Three organizations and 448 individuals support the
proposed rule, especially NMFS's decision to reduce the Area 1A TAC to
45,000 mt in 2008 and 2009.
Response: This action is unchanged from the proposed rule.
Comment 2: Two organizations and three vessel owners opposed the
Council's recommendation to reduce the Area 1A TAC to 50,000 mt for
2007-2009, and strongly opposed NMFS's further reduction of the Area 1A
TAC to 45,000 mt for 2008 and 2009. They argue that the Council's
recommendation was unnecessarily restrictive, in light of the stock's
status. They further argue that NMFS should not have relied on the Plan
Development Team's (PDT's) risk assessment in making its decision to
further reduce the Area 1A TAC to 45,000 mt because it was not peer-
reviewed, and was overly conservative. They disagreed that the
Councils' and NMFS's concern about the retrospective pattern in the
stock assessment is an appropriate reason to reduce the Area 1A TAC.
They argued that the 29,000-mt buffer between ABC and OY was intended
to account for the retrospective pattern and that it is, therefore,
scientifically inappropriate to further reduce the Area 1A TAC. The
commenters argue that the Council's specifications document pointed out
that trawl survey results are highly variable, and that no trends are
apparent from the most recent years of the survey across all strata.
The commenters state that encounter rates are increasing, rather than
declining, and a broader size distribution is evident; and that both of
these trends indicate a healthy resource. One organization stated that
it is misleading for NMFS to state that there
[[Page 17809]]
is considerable overlap between the inshore stock component and Area
1A.
One organization supported the reduction of the Area 1A TAC to
50,000 mt, but not to 45,000 mt in 2008 and 2009. They argue that the
retrospective pattern described by the Transboundary Resource
Assessment Committee (TRAC) applies to the stock as a whole, and not
individual stock components, and that the 29,000-mt buffer between ABC
and OY addresses the issue. They stated that the reduction in the Area
1A TAC to 45,000 mt and commensurate increase in the Area 3 TAC does
not account for the retrospective pattern, because it maintains OY at
the same level. They also argued that only the NMFS fall survey shows a
decline in abundance and biomass, and the other surveys are either
increasing or variable and stable. They noted that the PDT suggested
that encounter rates may be a better indicator of stock status for
herring, and that the Northeast Fisheries Science Center (NEFSC) fall
surveys are not showing a decline in the encounter rates, and the
Massachusetts inshore survey is showing an increase in encounter rates.
One organization opposed the reduction of Area 1A TAC, but provided
no additional rationale. One vessel owner argued that the industry was
not allowed to participate in the Advisory Panel's decisionmaking
during the specifications-setting process.
Response: The herring stock is in good shape. However, both the
Council and NMFS agree that, while the overall stock is healthy, there
is a clear need to be precautionary with the inshore component of the
stock. This is directly related to the establishment of the Area 1A TAC
because, contrary to some comments, there is substantial overlap
between the inshore stock component and Area 1A. The inshore component,
at different times of year, is distributed throughout Areas 1A, 1B, and
2. Based on the stock mixing ratios employed in the specifications
document (and in the FMP), it is reasonable to state that there is a
considerable amount of overlap between the inshore stock component and
Area 1A. The specifications document estimates that, in the summer, 50
percent of the catch from Area 1A comes from the inshore component. In
the winter, 100 percent of the catch in Area 1A, and 20 percent of the
catch in Area 2, is assumed to come from the inshore component of the
resource. Removals from Area 1B are assumed to be composed of 30
percent of the inshore component at all times of the year.
Several aspects of the specifications analyses provided a strong
basis for NMFS to enact the Area 1A TACs specified in this action.
Three elements in particular contributed to NMFS's determination that
the 2008-2009 TACs should be set lower than recommended by the Council.
The Council's Scientific and Statistical Committee (SSC) met in
2003 to consider the status of the herring stock and found, among other
things, that ``no severe declines in the stock complex should be
expected by maintaining current levels of catches over the short-term;
however, the current concentration of harvest in the inshore Gulf of
Maine is of concern and may be excessive.'' Thus, NMFS concluded that
the issue is not whether there is a need for more caution when
establishing the Area 1A TAC, but rather, how much caution is
necessary.
Both the Council and NMFS agreed that the available data and
concerns warranted a significant reduction in the Area 1A TAC over the
next 3 years. NMFS, however, concluded that the Council's proposal, to
set the Area 1A TAC at 50,000 mt, did not go far enough to protect the
stock in Area 1A.
NMFS also concluded that the retrospective pattern in the stock
assessment, which overestimates biomass and underestimates fishing
mortality in the terminal year of the assessment, argues for caution.
NMFS concluded that for the stock as a whole, the buffer of 29,000 mt
between ABC (maximum OY) and OY specified in this action would help
ensure that adequate spawning stock biomass (SSB) is available to
produce strong recruitment in the future. However, the retrospective
pattern indicates that, as more data are collected and analyzed, the
stock, including the inshore stock component, will be found to be not
as robust as current data imply.
Finally, the PDT's risk assessment provides a useful tool for
evaluating TAC alternatives. The risk assessment is a tool that the
Council asked the PDT to provide, and it was presented and debated by
the PDT members, the Herring Advisory Panel (AP), and the Herring
Committee, as well as the Council. According to the risk assessment,
setting the Area 1A TAC at 45,000 mt for 2008-2009 will provide a
slightly improved chance of producing exploitation rates that are more
consistent with Fmsy for the stock component, within a range of
realistic stock mixing ratios. Therefore, NMFS finds that the SSC
advice, the retrospective pattern in the stock assessment, and the
conclusions of the PDT's risk assessment combine to make a sound case
for specifying the Area 1A TAC at 45,000 mt in fishing years 2008 and
2009.
The commenters correctly characterize the variability of the trawl
survey data and encounter rates. While NMFS acknowledges these points,
it does not conclude that they overcome the concerns noted above. More
specifically, although some of the encounter rates do not indicate a
decline in stock status, they are just one of the indicators that the
Council and NMFS needs to rely on in determining the appropriate levels
for the various TACs. As mentioned above, taken together, the SSCs
advice, the significant retrospective pattern in the stock assessment,
and the PDT's risk assessment, even in the face of some positive or
stable encounter rates, justify the precautionary approach being taken
in this rule.
NMFS does not share the commenters' concerns about the use of the
PDT's risk assessment. PDTs are established by the Council specifically
to offer technical advice that will assist in making sound fishery
management decisions. The current process for obtaining the PDT's
advice does not include an additional formal peer review of that
advice. A certain amount of informal peer review is built into the PDT
process by virtue of its membership and the debates that take place at
PDT meetings, the Council's committee meetings, and Council meetings.
An additional layer of informal peer review takes place within NMFS,
when the specifications package, including the PDT's products, are
reviewed by NMFS staff.
The perception that the industry was not allowed to participate in
the AP's deliberations is not accurate. Not only is the AP comprised of
industry members, but all of its meetings were public meetings, for
which public notice was provided. At those meetings a variety of
industry members contributed their thoughts and ideas to the process,
although not all of their suggestions were ultimately adopted.
Comment 3: Two organizations argued that the reduction of the Area
1A TAC to 45,000 mt is not justified. They also argued that the PDT
analysis was presented to the Council at the last minute and that
participants in the fishery did not have adequate opportunity to review
and comment on it. One commenter argued that the use of this new
analysis appears contrary to the recent Congressional reauthorization
of the Magnuson-Stevens Fishery Conservation and Management Act
(Magnuson-Stevens Act), which specifies in section 302(g) that, ``The
Secretary and each Council may
[[Page 17810]]
establish a peer review process for that Council for scientific
information used to advise the Council about the conservation and
management of the fishery.'' Finally, this commenter argued that the
assumption in the specifications that the New Brunswick (NB) weir
fishery will catch 20,000 mt annually is an overestimate and,
therefore, it serves to provide an additional level of caution in the
specifications.
Response: The justification for setting the Area 1A TAC at 45,000
mt and the concerns about the PDT's risk assessment are addressed in
the response to Comment 2. NMFS notes that the Council process provided
several opportunities for public comment, including comment on the risk
assessment.
The new Magnuson-Stevens Act requirement is not retroactively
applicable to the process the Council followed to develop these herring
specifications.
The Council adopted the estimate that the NB weir fishery will land
20,000 mt annually after public debate. Though in recent years landings
by this fishery have not attained 20,000 mt, the Council and NMFS
concluded it is a reasonable estimate. Historical catches in the NB
weir fishery were much higher than those in recent years, and exceeded
20,000 mt in many years prior to 1995. Landings of herring in the NB
weir fishery average 22,475 mt for 1978-2005, despite the fact that the
2005 landings are currently estimated to have been about 13,000 mt.
Comment 4: Five vessel owners pointed out that there is no stock
assessment for the inshore component and, therefore, the target and
threshold fishing mortality rates for the inshore stock component
remain uncertain. Because of this, the owners argue that reducing the
Area 1A TAC based on a concern that the Council's recommendations for
2008 and 2009 would be only marginally successful at producing an
exploitation rate consistent with Fmsy is not justified,
because the Fmsy for the inshore component remains
uncertain. Furthermore, these owners pointed out that, although the
TRAC assessment estimated that the inshore component of the stock
represents 18 percent of the total stock biomass, the TRAC assessment
does not provide guidance on the TAC allocations by management area or
the mixing rates between stock components. The owners find the use of
the 18 percent value to be problematic, and cast doubt on the
usefulness of the PDT's risk assessment because it is not peer-
reviewed. The risk assessment should not, they contend, be used as a
justification for draconian cuts.
Response: The commenters are correct that the stock assessment does
not provide specific fishing mortality target and threshold rates for
the inshore stock component or the specification of management area
TACs. However, NMFS concluded that it is appropriate to use the risk
assessment and the TRAC estimate that the inshore stock component
represents 18 percent of the total biomass, for reasons outlined in
detail in the response to Comment 2. The stock mixing ratios used in
the risk assessment are, as the specifications document points out,
supported by the best available scientific information.
Comment 5: Five organizations argued that the proposed reallocation
of 5,000 mt from Area 1A to Area 3 should, instead, be a reallocation
of the same amount into a reserve for Area 2. The rationale offered is
that a higher percentage of the Area 2 TAC has been taken in recent
years than of the Area 3 TAC. The establishment of such a reserve
would, the commenters argue, increase the amount of herring available
to the Atlantic mackerel fishery, which has an incidental catch of
herring. This would reduce the likelihood of a closure of the herring
fishery in Area 2. The commenters believe that a herring closure would
de facto close the mackerel fishery in that area because vessels would
not fish in the area for mackerel if they could not also retain more
than 2,000 lb (907.2 kg) of herring.
Response: There are two reasons for transferring the 5,000 mt from
Area 1A to Area 3. First, since Area 3 fish are assumed to come
entirely from the offshore component of the stock, the addition of
5,000 mt to that Area's TAC will not impact the status of the inshore
component. Second, this reallocation will increase opportunities for
the fleet to fish for herring in Area 3 and, therefore, support one of
the FMP's goals, which is to provide for the orderly development of the
offshore herring fishery. In contrast, because of mixing of the
subcomponents of the stock, a shift of 5,000 mt from Area 1A to Area 2
would still allow the fishery to harvest from the inshore stock
component.
On a practical level, the Area 2 TAC has never been fully
harvested. In 2006, roughly 22,000 mt of herring was landed from this
area, while in the 4 prior years, landings from the area ranged from
11,000 mt to 16,000 mt. In light of this history, the 30,000 mt
allocated to Area 2 would appear unlikely to constrain the mackerel
fishery. The Council has the option of reviewing information relating
to the herring stock and fishery in 2007 and revising the Area 2 TAC
for 2008-2009, if warranted.
Comment 6: Two organizations urged that a portion of the DAH be
set-aside for use in value-added food grade products, and that such an
allocation would be consistent with the allocation of 20,000 mt for
USAP. These commenters also urged NMFS to establish three different
fishing seasons within Area 1A, and to apportion the TAC among those
seasons to extend the fishing season in Area 1A, achieve OY, and more
effectively protect pre-spawning herring.
Response: These suggestions would require amendment of the Herring
FMP, which defines the allocations that must be recommended by the
Council and enacted by NMFS, and are therefore outside the scope,
purpose, and authority of this action. Such changes may be pursued
through the Council process.
Comment 7: Two organizations argued that the Council's decision to
review the new survey data during 2007 and determine whether
adjustments should be made to the specifications for the 2008 and 2009
fishing years was sufficiently precautionary and should be allowed to
proceed. One organization believed that NMFS's revision of the
allocations for 2008-2009 precluded the Council from conducting a
review of the fishery during the 3-year specification period.
Response: NMFS's decision to reduce the Area 1A TAC to 45,000 mt
for the 2008 and 2009 fishing years has no bearing on the review
process that the Council stated that it plans to conduct during 2007.
That review is expected to take place, and the Council is at liberty to
recommend changes to the specifications for 2008 and/or 2009 based on
its review, if warranted.
Comment 8: Five vessel owners supported the implementation of the
status quo specifications for the herring fishery, which would set OY
at 150,000 mt, the Area 1A TAC at 60,000 mt, and the Area 3 TAC at
50,000 mt. They argue that the recent landings levels of around 100,000
mt are sustainable. They note that the TRAC report supports this view,
and that the PDT analysis indicates that all of the alternatives,
including the status quo, are projected to result in removals of the
inshore component that are less than the historical (1995-2006)
removals within a reasonable range of stock mixing assumptions.
Response: The commenters are correct in noting that the TRAC
concluded that removals at current levels (around 100,000 mt per year
for the past 15 years) are sustainable. They are also
[[Page 17811]]
correct that the PDT's risk assessment indicated that setting the TACs
at the status quo level was projected to result in removals from the
inshore stock component that are less than historical removals for the
period 1995-2005, during the winter (January-March; August-December).
However, the PDT's risk assessment was not as clear cut for the summer
period (April-July), where it showed that the status quo TACs would
generate removals that would be at or below historical removals in
about 50 percent of the possible scenarios. Both the Council's
recommended TACs and the TACs established by this action would be more
risk-averse than the status quo during the summer period, when a large
amount of the Area 1A catch is taken.
The commenters failed to note that there was a second part to the
PDT's risk assessment, which evaluated the success of proposed TAC
alternatives in achieving an exploitation rate that equates to
Fmsy for the herring stock. As noted in the response to
Comment 2, this aspect of the risk assessment was one of the reasons
that both the Council and NMFS concluded that it was appropriate to
make a significant reduction in the Area 1A TAC to reduce the risk of
overfishing the inshore stock component.
Comment 9: One organization argued that, based on the TRAC results
and reasonable assumptions about stock component mixing rates, the Area
1A TAC should be set between 35,000-42,000 mt. Furthermore, this
organization does not support the addition of 5,000 mt to the Area 3
TAC, and argues that, at most, the Area 3 TAC should be 55,000 mt. The
commenter argues that, because the natural mortality rate used by the
TRAC in its assessment model is not accurate and might significantly
underestimate natural mortality, NMFS has not accurately estimated the
amount of herring that can be safely removed from the ecosystem and
that, as a result, NMFS should be more precautionary in setting the
herring specifications.
Response: The PDT stated that if it may be possible to apply a
fishing mortality rate to an average biomass for the inshore stock
component (assuming that it comprises 18 percent of total biomass), and
estimate a TAC specifically for the inshore stock component. Using this
approach would likely result in a TAC for the inshore stock component
of about 35,000 mt - 42,000 mt. However, the PDT also stated that a TAC
for the inshore stock component does not equate to a TAC for Area 1A,
as fish from both the inshore and offshore component are caught in
Areas 1A, 1B, and 2.
Regarding the commenter's contention that the natural mortality
rate used in the TRAC assessment is not accurate, the TRAC investigated
values for natural mortality other than 0.2, but deemed that 0.2 was
the appropriate value to use in the stock assessment. The peer-reviewed
TRAC results constitute the best available scientific information on
this point.
NMFS notes that Fmsy for the stock was estimated at 0.31 by the
TRAC. The analysis of the stockwide F associated with the
specifications estimates F's of 0.18 in 2007; 0.197 in 2008, and 0.221
in 2009. NMFS concludes that these fishing mortality estimates are
sufficiently precautionary.
Comment 10: Five vessel owners argued that the perceived declines
in the inshore component, based on the incorporation of recent data
(2004 and 2005) from the NMFS trawl survey, appears to be a rush to
judgment. They pointed out that, in 2006, herring fishermen reported
very high inshore biomass and that, based on a personal communication
with NEFSC staff, the fall 2006 survey results indicate a rebound to
previous levels.
Response: The PDT noted the impact that recent data has on overall
trends for the inshore component; however it also placed that data
within its proper context, stating that, ``While data specific to the
inshore component of the stock is limited and the Herring PDT cannot
make a status determination based on bottom trawl indices alone, a
change in the direction of the trend line is an important
consideration.'' The Council's 2007 review will consider any upated
survey data and, if the results indicate a change in the apparent trend
of recent years, then it could result in recommendations for TAC
adjustments in 2008-2009. While NMFS took recent trawl survey
information into account in taking this action, there were several
factors that led NMFS to specify the Area 1A TAC at 45,000 mt for 2008-
2009, as discussed in the response to Comment 2.
Comment 11: Five vessel owners argued that the 10,000-15,000 mt
reduction of the Area 1A TAC will have greater economic impacts than
the revenue loss estimates of $136,350-204,500 per vessel for purse
seine vessels. They contend that it is incorrect to assume that the
reduced catch in Area 1A can be made up from Area 3. They explain that
vessel size and weather make it difficult for their vessels to work
offshore and make up for reduced landings from Area 1A.
Response: The analysis of the economic impacts of the proposed TACs
takes into account the same points made by the commenter. The specific
per-vessel revenue impacts cited by the commenter are part of the
analysis of revenue impacts on vessels that have harvested herring from
Area 1A in the past, and are likely to qualify for the limited access
permit established by Amendment 1. The analysis presumes that these
vessels will continue to harvest the same proportion of the Area 1A TAC
as in the past. The analysis notes that there are several things that
could affect this assumption, notably that the reduced TAC may create
an incentive for vessel owners to compete more aggressively for the
reduced Area 1A TAC, thus altering the proportion of fish available to
past participants. The analysis also notes that, while there are
opportunities to harvest fish from other management areas to compensate
for the reduction in Area 1A, this may not be possible for all vessels.
It notes that there are a number of reasons it may not be possible for
all vessels to fish in other areas, particularly offshore Areas 2 and
3, because the size of some vessels creates safety concerns, and
because there are higher operating costs associated with longer trips,
notably the costs associated with additional steaming time and
associated fuel costs.
Comment 12: One organization argued that, because of the mixing
between offshore and inshore components during the spring, only the
fall surveys should be considered as an indicator of the status of the
inshore stock component. It also argued that a number of the survey
results, as well as observed encounter rates, indicate that the health
of the stock is not in decline.
Response: Overall, the herring stock is in good shape, but for
reasons outlined in the response to Comment 2 there are concerns about
the inshore stock component that resulted in the reduction of the Area
1A TAC.
Classification
This action is authorized by 50 CFR part 648 and has been
determined to be not significant for purposes of Executive Order 12866.
A FRFA was prepared. The FRFA incorporates the IRFA, a summary of
the signficant issues raised by the public comments in response to the
IRFA, NMFS responses to those comments, and a summary of the analyses
completed to support the action. A copy of the analyses is available
from NMFS (see ADDRESSES).
A description of the reasons for this action, the objectives of
this action, and the legal basis for this final rule is found
[[Page 17812]]
in the preambles to the proposed rule and this final rule and is not
repeated here.
Statement of Need for this Action
The purpose of this action is to establish specifications to
conserve and manage the herring resource for the period 2007-2009, as
required by the FMP.
A Summary of the Significant Issues Raised by the Public Comments in
Response to the IRFA, a Summary of the Assessment of the Agency of Such
Issues, and a Statement of Any Changes Made in the Proposed Rule as a
Result of Such Comments
NMFS received 460 comments on the proposed specifications. Only one
comment was specific to the IRFA. Comment 12 outlines concerns
expressed by five vessel owners that the analysis of the Area 1A TACs
underestimated the economic impacts they would experience due to the
reductions in the allocation for the area. NMFS' assessment of the
issues raised by this comment is contained in the preamble and not
repeated here. The comment did not result in any changes to the Area 1A
TAC, which was reduced for biological reasons.
Description and Estimate of Number of Small Entities to Which the Rule
Will Apply
During the 2005 fishing year, 143 vessels landed herring, 33 of
which averaged more than 2,000 lb ( 907 kg) of herring per trip. The
Small Business Administration's size standard for small commercial
fishing entities is $4 million in gross sales. Thus, all the entities
participating in this fishery are considered small entities, as defined
in section 601 of the RFA. Therefore, there are no disproportionate
economic impacts between large and small entities.
Description of Projected Reporting, Recordkeeping, and Other Compliance
Requirements
This action does not contain any new collection-of-information,
reporting, recordkeeping, or other compliance requirements.
Description of the Steps the Agency Has Taken to Minimize the
Significant Economic Impact on Small Entities Consistent with the
Stated Objective of Applicable Statutes, including a Statement of the
Factual, Policy, and Legal Reasons for Selecting the Alternative
Adopted in the Final Rule and Why Each of the Other Significant
Alternatives to the Rule Considered by the Agency which Affect the
Impact on Small Entities was Rejected
The economic impacts of this action were assessed by the Council
and NMFS in an analysis that compares the alternatives considered to
the herring landings made in 2005, the most recent year for which
complete data are available. From a fishery-wide perspective, these
specifications are not expected to produce a negative economic impact
to vessels prosecuting the fishery because it allows for landings
levels that are significantly higher than the landings in recent years.
The 2007-2009 specifications should allow for incremental growth in the
industry, while appropriately addressing biological concerns. However,
because of the allocation of the management area TACs, and the
reduction in the Area 1A TAC in particular, these specifications could
have a negative impact on various industry participants, despite the
fact that overall landings levels could be higher than in recent years.
The specification of OY and DAH is 145,000 mt for 2007-2009. While
higher levels of OY were considered (150,000 mt and 170,000 mt) the OY
of 145,000 mt will allow an annual increase of up to 51,610 mt in
herring landings compared to the 93,390 mt landed in 2005. This will
generate $10.4 million in revenues, based on an average price (in 2005)
of $202/mt. Therefore, there are no negative economic impacts
associated with the specification of OY in this action. Individual
vessels could increase their revenues under the proposed 2007-2009
specifications, depending on the number of vessels participating in the
fishery, which will become a limited access fishery with the
implementation of Amendment 1 to the FMP on June 1, 2007.
Several other specifications established by this action would also
allow an increase in revenue to industry participants when compared to
the 2005 landings. These include DAH and DAP, which are specified at
145,000 mt and 141,000 mt, respectively; USAP, which is specified at
20,000 mt; the Area 1B TAC, which is specified at 10,000 mt; the Area 2
TAC, which is specified at 30,000 mt; and the Area 3 TAC, which is
specified at 55,000 mt in 2007 and 60,000 mt in 2008-2009. In each
instance, there are no negative economic impacts associated with these
specifications because they would allow industry participants to
harvest and/or process more herring than in 2005. There are no
potential economic impacts associated with the allocation for JVPt of
zero, because it is unchanged from 2005.
The only specification that could constrain the industry when
compared to landings and revenue in 2005 is reduction of the Area 1A
TAC to 50,000 mt in 2007, and 45,000 mt in 2008 and 2009. The impacts
of these reductions were analyzed for the purse seine fleet, the single
midwater trawl fleet, and the paired midwater trawl fleet.
In 2005, the currently active purse seine fleet caught 27 percent
of the Area 1A TAC. With a 10,000-15,000-mt reduction in the Area 1A
TAC, if the proportion of the herring catch by the purse seine fleet
remains the same and the decrease in the Area 1A TAC cannot be made up
from fishing in other areas, there would be a 2,700-mt loss in catch
under this action in 2007, and a 4,050-mt loss in catch in 2008 and
2009. Using the 2005 average price of herring of $202 per metric ton,
this loss in catch would be worth $545,400 and $818,000, respectively,
across the sector (there are four vessels in the currently active purse
seine fleet). To make up for such a loss, these vessels would have to
either increase their proportion of the herring catch in Area 1A
relative to midwater trawlers, or move to other areas. There were no
landings from Area 3 by these purse seine vessels in 2005, likely
reflecting the fact that the vessels are too small to fish in these
offshore areas. Moving offshore would also entail additional operating
costs because the trips would be longer.
The impact of the 10,000-15,000-mt decrease in the Area 1A TAC on
the single midwater trawl fleet is difficult to predict, because the
Purse Seine/Fixed Gear (PS/FG) only area established by Amendment 1
will eliminate single midwater trawl vessels from Area 1A during the
most productive part of the Area 1A fishery (June through September).
The establishment of a PS/FG only area might intensify the race to fish
in Area 1A, as midwater trawl vessels (single and paired) may try to
catch more fish from the area prior to the closure to trawling on June
1.
If herring are plentiful in Area 1A during the spring (Area 1A
catches increase in May, historically), the single midwater trawlers
may be able to maintain their historical proportion of the Area 1A TAC.
However, it is likely
[[Page 17813]]
that purse seine vessels and midwater pair trawl vessels would also
participate in the pre-June race in order to keep their landings on par
with previous years. In addition, single midwater trawl vessels might
convert to purse seine gear in order to fish in Area 1A in the summer.
In 2005, the currently active single midwater trawl fleet caught 18
percent of the Area 1A TAC. If the proportion of the herring catch by
the single midwater trawl fleet remains the same, and the decrease in
the Area 1A TAC cannot be made up from fishing in other areas, there
would be a 1,800-mt loss in catch under this action during 2007, and a
2,700-mt loss in catch in 2008 and 2009. Using the 2005 average price
of herring of $202 per metric ton, this loss in catch would be worth
$363,600 and $545,400, respectively, across the sector (there are four
vessels that were active in Area 1A from 2003-2005 in the single
midwater trawl fleet). To make up for such a loss, the single midwater
trawl vessels would have to either increase their proportion of the
herring catch in Area 1A relative to purse seine vessels, or move to
other areas. Moving to offshore areas may be problematic for two of the
four single midwater trawl vessels, since these two are relatively
smaller vessels and landed herring only from Area 1A during 2003
through 2005. The other two vessels are somewhat larger and have Area 3
catch history, so their loss of Area 1A catch may be mitigated by their
ability to fish in Area 3. If the single midwater trawl vessels make up
their catch in Areas 2 and 3, the vessel operating cost will increase
because the trips will be longer.
With decreases in the Area 1A TAC of 10,000 mt to 15,000 mt under
this action, the impact on the midwater pair trawl fleet could also be
large. It is difficult to predict what the impact will be on the
midwater pair trawl fleet, because these vessels will also be excluded
from Area 1A for the period June-September due to the PS/FG only
measure. In 2005, the currently active pair trawl fleet caught 55
percent of the Area 1A TAC. If the proportion of the herring catch by
the pair trawl fleet remains the same and the decrease in the Area 1A
TAC cannot be made up from fishing in other areas, there would be a
5,500-mt loss in catch under this action in 2007, and a 8,250-mt loss
in 2008 and 2009. Using the 2005 average price of herring of $202 per
metric ton, this catch is worth $1,111,000 and $1,666,500 respectively,
across the sector (there are 12 vessels in the pair trawl fleet that
were active from 2003-2005). To make up for such a loss, pair trawl
vessels would have to either increase their proportion of the herring
catch in Area 1A or move to other areas. All pair trawl vessels have
Area 3 catch history, so their loss of Area 1A catch may be mitigated
by their ability to fish in Area 3. If the pair trawl vessels make up
their catch in Areas 2 and 3, the vessel operating cost will increase
because the trips would be longer.
The 10,000-mt to 15,000-mt reduction in TAC in Area 1A may cause
participants using all 3 gear types to increase their fishing activity
in Area 1B. The Area 1B TAC has not been reached every year, and only
60 percent was harvested in 2005. Since Area 1B is farther from shore
than Area 1A, vessel operating costs would increase because trips would
be longer. Harvesting in Area 1B will only provide limited relief for
vessels impacted by the reduction in the Area 1A TAC since the TAC is
limited to 10,000 mt.
There were seven alternatives considered. Three of the alternatives
would have set the Area 1A TAC at 60,000 mt. They were rejected because
the biological concerns about the inshore herring stock component
require a significant reduction in harvest within Area 1A. More
specifically, NMFS concluded that the SSC's advice, the retrospective
pattern in the stock assessment, and the conclusions of the PDT's risk
assessment combine to make a sound case for being precautionary about
protecting the inshore component and for specifying the Area 1A TAC at
45,000 mt.
One alternative would have set the Area 1A TAC at 50,000 mt for all
three years. This was rejected for the reasons cited above; namely,
that the SSC's advice, the retrospective pattern in the stock
assessment, and the conclusions of the PDT's risk assessment combine to
make a sound case for being precautionary about protecting the inshore
component and for specifying the Area 1A TAC at 45,000 mt.
Two of the alternatives would have reduced the Area 1A TAC to
45,000 mt for all three years. These were rejected because NMFS
believed that it is sufficient to achieve biological objectives to
implement the 45,000 mt TAC for 2008-2009, and establish the 2007 TAC
at 50,000 mt, consistent with action taken by the states under the
Atlantic States Marine Fisheries Commission's Interstate Fisheries
Management Plan for Atlantic Sea Herring. The preferred alternative was
selected because the SSC's advice, the retrospective pattern in the
stock assessment, and the conclusions of the PDT's risk assessment
combine to make a sound case for specifying the Area 1A TAC at 45,000
mt in fishing years 2008 and 2009.
Small Entity Compliance Guide
Section 212 of the Small Business Regulatory Enforcement Fairness
Act of 1996 states that, for each rule, or group of related rules, for
which an agency is required to prepare a FRFA, the agency shall publish
one or more guides to assist small entities in complying with the rule
and shall designate such publications as ``small entity compliance
guides.'' The agency shall explain the actions a small entity is
required to take to comply with a rule or group of rules. As part of
this rulemaking process, a small entity compliance guide will be sent
to all holders of permits issued for the herring fishery. In addition,
copies of this final rule and guide (i.e., permit holder letter) are
available from the Regional Administrator (see ADDRESSES) and may be
found at the following web site: https://www.nero.noaa.gov.
Authority: 16 U.S.C. 1801 et seq.
Dated: April 2, 2007.
John Oliver,
Deputy Assistant Administrator for Operations, National Marine
Fisheries Service.
[FR Doc. E7-6648 Filed 4-9-07; 8:45 am]
BILLING CODE 3510-22-S