Magnuson-Stevens Fishery Conservation and Management Act Provisions; Fisheries of the Northeastern United States; Northeast Region Standardized Bycatch Reporting Methodology Omnibus Amendment, 4736-4758 [E8-1436]
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b. In paragraph (n)(4), revise the first
sentence following the heading and
paragraph (n)(4)(v) and add paragraph
(n)(4)(xiii) to read as set forth below:
I
§ 17.84
Special rules—vertebrates.
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(n) * * *
(3) * * *
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Legally present—A Person is legally
present when (1) on their own property,
(2) not trespassing and has the
landowner’s permission to bring their
stock animal or dog on the property, or
(3) abiding by regulations governing
legal presence on public lands.
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Stock animal—A horse, mule,
donkey, llama, or goat used to transport
people or their possessions.
Unacceptable impact—Impact to
ungulate population or herd where a
State or Tribe has determined that
wolves are one of the major causes of
the population or herd not meeting
established State or Tribal management
goals.
Ungulate population or herd—An
assemblage of wild ungulates living in
a given area.
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(4) Allowable forms of take of gray
wolves. The following activities, only in
the specific circumstances described
under this paragraph (n)(4), are allowed:
Opportunistic harassment; intentional
harassment; take on private land; take
on public land except land administered
by National Parks; take in response to
impacts on wild ungulate populations;
take in defense of human life; take to
protect human safety; take by
designated agents to remove problem
wolves; incidental take; take under
permits; take per authorizations for
employees of designated agents; take for
research purposes; and take to protect
stock animals and dogs. * * *
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(v) Take in response to wild ungulate
impacts. If wolf predation is having an
unacceptable impact on wild ungulate
populations (deer, elk, moose, bighorn
sheep, mountain goats, antelope, or
bison) as determined by the respective
State or Tribe, a State or Tribe may
lethally remove the wolves in question.
(A) In order for this provision to
apply, the State or Tribes must prepare
a science-based document that:
(1) Describes the basis of ungulate
population or herd management
objectives, what data indicate that the
ungulate population or herd is below
management objectives, what data
indicate that wolves are a major cause
of the unacceptable impact to the
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ungulate population or herd, why wolf
removal is a warranted solution to help
restore the ungulate population or herd
to State or Tribal management
objectives, the level and duration of
wolf removal being proposed, and how
ungulate population or herd response to
wolf removal will be measured and
control actions adjusted for
effectiveness;
(2) Demonstrates that attempts were
and are being made to address other
identified major causes of ungulate herd
or population declines or the State or
Tribe commits to implement possible
remedies or conservation measures in
addition to wolf removal; and
(3) Provides an opportunity for peer
review and public comment on their
proposal prior to submitting it to the
Service for written concurrence. The
State or Tribe must:
(i) Conduct the peer review process in
conformance with the Office of
Management and Budget’s Final
Information Quality Bulletin for Peer
Review (70 FR 2664, January 14, 2005)
and include in their proposal an
explanation of how the bulletin’s
standards were considered and satisfied;
and
(ii) Obtain at least five independent
peer reviews from individuals with
relevant expertise other than staff
employed by a State, Tribal, or Federal
agency directly or indirectly involved
with predator control or ungulate
management in Idaho, Montana, or
Wyoming.
(B) Before we authorize lethal
removal, we must determine that an
unacceptable impact to wild ungulate
populations or herds has occurred. We
also must determine that the proposed
lethal removal is science-based, will not
contribute to reducing the wolf
population in the State below 20
breeding pairs and 200 wolves, and will
not impede wolf recovery.
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(xiii) Take to protect stock animals
and dogs. Any person legally present on
private or public land, except land
administered by the National Park
Service, may immediately take a wolf
that is in the act of attacking the
individual’s stock animal or dog,
provided that there is no evidence of
intentional baiting, feeding, or
deliberate attractants of wolves. The
person must be able to provide evidence
of stock animals or dogs recently (less
than 24 hours) wounded, harassed,
molested, or killed by wolves, and we
or our designated agents must be able to
confirm that the stock animals or dogs
were wounded, harassed, molested, or
killed by wolves. To preserve evidence
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that the take of a wolf was conducted
according to this rule, the person must
not disturb the carcass and the area
surrounding it. The take of any wolf
without such evidence of a direct and
immediate threat may be referred to the
appropriate authorities for prosecution.
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Dated: December 27, 2007.
Kenneth Stansell,
Acting Director,
U.S. Fish and Wildlife Service.
[FR Doc. 08–334 Filed 1–24–08; 8:45 am]
BILLING CODE 4310–55–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 070627217–7523–02]
RIN 0648–AV70
Magnuson-Stevens Fishery
Conservation and Management Act
Provisions; Fisheries of the
Northeastern United States; Northeast
Region Standardized Bycatch
Reporting Methodology Omnibus
Amendment
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
SUMMARY: NMFS is implementing
approved management measures
contained in the Standardized Bycatch
Reporting Methodology (SBRM)
Omnibus Amendment (SBRM
Amendment) to the Fishery
Management Plans (FMPs) of the
Northeast Region, developed by the
Mid-Atlantic and New England Fishery
Management Councils (Councils). The
SBRM Amendment establishes an
SBRM for all 13 Northeast Region FMPs,
as required under the MagnusonStevens Fishery Conservation and
Management Act (Magnuson-Stevens
Act). The measures include: Bycatch
reporting and monitoring mechanisms;
analytical techniques and allocation of
at-sea fisheries observers; an SBRM
performance standard; a review and
reporting process; framework
adjustment and annual specifications
provisions; a prioritization process; and
provisions for industry-funded
observers and observer set-aside
programs.
This final rule is effective
February 27, 2008.
DATES:
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Copies of the SBRM
Amendment, and of the Environmental
Assessment (EA), with its associated
Finding of No Significant Impact
(FONSI), and the Regulatory Impact
Review (RIR), are available from Daniel
T. Furlong, Executive Director, MidAtlantic Fishery Management Council,
Room 2115, Federal Building, 300 South
New Street, Dover, DE 19901–6790; and
from Paul J. Howard, Executive Director,
New England Fishery Management
Council, 50 Water Street, Newburyport,
MA 01950. The EA/FONSI/RIR is also
accessible via the Internet at https://
www.nero.noaa.gov.
FOR FURTHER INFORMATION CONTACT:
Michael Pentony, Senior Fishery Policy
Analyst, 978–281–9283.
SUPPLEMENTARY INFORMATION:
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ADDRESSES:
Background
This final rule implements approved
management measures contained in the
Northeast Region Omnibus SBRM
Amendment, which was approved by
NMFS on behalf of the Secretary of
Commerce (Secretary) on October 22,
2007. A proposed rule for this action
was published on August 21, 2007 (72
FR 46588), with public comments
accepted through September 20, 2007. A
subsequent publication extended this
comment period through September 24,
2007 (72 FR 53751).
Section 303(a)(11) of the MagnusonStevens Act requires that all FMPs
‘‘establish a standardized reporting
methodology to assess the amount and
type of bycatch occurring in the
fishery.’’ In 2004, several conservation
organizations challenged the approval of
two major amendments to Northeast
Region FMPs. In ruling on these suits,
the U.S. District Court for the District of
Columbia found that the FMPs did not
clearly establish an SBRM as required
under the relevant section of the
Magnuson-Stevens Act and remanded
the amendments back to the agency to
fully develop and establish the required
SBRM [See, Oceana, Inc., v. Evans,
2005, WL 555416 (D.D.C. Mar 9,
2005)(Oceana I); and Oceana, Inc., v.
Evans, 384 F. Supp 2d 203 (D.D.C.
2005)(Oceana II)]. In particular, the
Court found that the amendments (1)
failed to fully evaluate reporting
methodologies to assess bycatch, (2) did
not mandate an SBRM, and (3) failed to
respond to potentially important
scientific evidence.
In response, the Councils, working
closely with NMFS, undertook
development of a remedy that would
address all Northeast Region FMPs. In
January 2006, development began on the
Northeast Region Omnibus SBRM
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Amendment. This amendment covers 13
FMPs, 39 managed species, and 14 types
of fishing gear. The purpose of the
amendment is to: Explain the methods
and processes by which bycatch is
currently monitored and assessed for
Northeast Region fisheries; determine
whether these methods and processes
need to be modified and/or
supplemented; establish standards of
precision for bycatch estimation for all
Northeast Region fisheries; and, thereby,
document the SBRM established for all
fisheries managed through the FMPs of
the Northeast Region. The amendment
also responds to the ‘‘potentially
important scientific evidence’’ cited by
the Court in the two decisions
referenced above.
The Northeast Region SBRM
Amendment establishes an SBRM
comprised of seven elements: (1) The
methods by which data and information
on discards are collected and obtained;
(2) the methods by which the data
obtained through the mechanisms
identified in element 1 are analyzed and
utilized to determine the appropriate
allocation of at-sea observers; (3) a
performance measure by which the
effectiveness of the Northeast Region
SBRM can be measured, tracked, and
utilized to effectively allocate the
appropriate number of observer sea
days; (4) a process to provide the
Councils with periodic reports on
discards occurring in Northeast Region
fisheries and on the effectiveness of the
SBRM; (5) a measure to enable the
Councils to make changes to the SBRM
through framework adjustments and/or
annual specification packages rather
than full FMP amendments; (6) a
process to provide the Councils and the
public with an opportunity to consider,
and provide input into, the decisions
regarding prioritization of at-sea
observer coverage allocations; and (7) to
implement consistent, cross-cutting
observer service provider approval and
certification procedures and to enable
the Councils to implement either a
requirement for industry-funded
observers or an observer set-aside
program through a framework
adjustment rather than an FMP
amendment.
Bycatch Reporting and Monitoring
Mechanisms
The amendment maintains the status
quo methods by which data and
information on discards occurring in
Northeast Region fisheries are collected
and obtained. The Northeast Region
SBRM will employ sampling designs
developed to minimize bias to the
maximum extent practicable. The
Northeast Fisheries Observer Program
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(NEFOP) continues to serve as the
primary mechanism to obtain data on
discards in all Northeast Region
commercial fisheries managed under
one or more of the subject FMPs. All
subject FMPs will continue to require
vessels permitted to participate in said
fisheries to carry an at-sea observer
upon request, and all data obtained by
the NEFOP under this SBRM will be
collected according to the techniques
and protocols established and detailed
in the Fisheries Observer Program
Manual and the Biological Sampling
Manual. Data collected by the NEFOP
include, but are not limited to, the
following items: Vessel name; date/time
sailed; date/time landed; steam time;
crew size; home port; port landed;
dealer name; fishing vessel trip report
(FVTR) serial number; gear type(s) used;
number/amount of gear; number of
hauls; weather; location of each haul
(beginning and ending latitude and
longitude); species caught; disposition
(kept/discarded); reason for discards;
and weight of catch. These data are
collected on all species of biological
organisms caught by the fishing vessel
and brought on board, including species
managed under the subject FMPs, but
also including species of non-managed
fish, invertebrates, and marine plants.
To obtain information on discards
occurring in recreational fisheries
subject to a Northeast Region FMP, the
Northeast Region SBRM fully will
incorporate, to the extent practicable
and appropriate for the Region, all
surveys and data collection mechanisms
implemented by NMFS and affected
states as a result of the agency-wide
redesign of the Marine Recreational
Fisheries Statistics Survey (MRFSS)
Program.
Analytical Techniques and Allocation
of At-sea Fisheries Observers
The amendment substantially
expands and refines the status quo
methods by which the data obtained
through the mechanisms included above
are analyzed and utilized to determine
the appropriate allocation of at-sea
observers to fully incorporate all
managed species and all relevant fishing
gear types in the Northeast Region. Atsea fisheries observers will, to the
maximum extent possible and subject to
available resources, be allocated and
assigned to fishing vessels according to
the procedures established through the
amendment. All appropriate filters
identified in the amendment will be
applied to the results of the analysis to
determine the observer coverage levels
needed to achieve the objectives of the
SBRM.
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SBRM Performance Standard
The amendment is intended to ensure
that the data collected under the
Northeast Region SBRM are sufficient to
produce a coefficient of variation (CV)
of the discard estimate of no more than
30 percent, in order to ensure that the
effectiveness of the Northeast Region
SBRM can be measured, tracked, and
utilized to effectively allocate the
appropriate number of observer sea
days. Each year, the Regional
Administrator and the Science and
Research Director will, subject to any
external operational constraints, allocate
at-sea observer coverage to the
applicable fisheries of the Northeast
Region sufficient to achieve a level of
precision (measured as the CV) no
greater than 30 percent for each
applicable species and/or species group,
subject to the use of the filters noted
above.
SBRM Review and Reporting Process
The amendment requires an annual
report on discards occurring in
Northeast Region fisheries to be
prepared by NMFS and provided to the
Councils, and a report every 3 years that
evaluates the effectiveness of the
Northeast Region SBRM. Every 3 years,
the Regional Administrator and the
Science and Research Director will
appoint appropriate staff to work with
staff appointed by the Executive
Directors of the Councils to obtain and
review available data on discards and to
prepare a report assessing the
effectiveness of the Northeast Region
SBRM. This report will include, at a
minimum: (1) A review of the recent
levels of observer coverage in each
applicable fishery; (2) a review of recent
observed encounters with each species
in each fishery, and a summary of
observed discards by weight; a review of
the CV of the discard information
collected for each fishery; (4) an
estimate of the total discards associated
with each fishery; (5) an evaluation of
the effectiveness of the SBRM at
meeting the performance standard for
each fishery; (6) a description of the
methods used to calculate the reported
CVs and to determine observer coverage
levels, if those methods are different
from those described and evaluated in
the SBRM Amendment; (7) an updated
assessment of potential sources of bias
in the sampling program and analyses of
accuracy; and (8) an evaluation of the
implications for management of the
discard information collected under the
SBRM, for any cases in which the
evaluation performed for item 5
indicates that the performance standard
is not met. Once each year, the Science
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and Research Director will present to
the Councils a report on catch and
discards occurring in Northeast Region
fisheries, as reported to the NEFOP by
at-sea fisheries observers. This annual
discard report will include: (1) The
number of observer sea days scheduled
for each fishery, by area and gear type,
in each quarter; (2) the percent of total
trips observed, by gear type, in each
quarter; (3) the distribution of sea
sampling trips by gear type and
statistical area in each fishery; (4) the
observed catch and discards of each
species, by gear type and fishery, in
each quarter; and (5) the observed catch
and discards of each species, by gear
type and fishery, in each statistical area.
Framework Adjustment and/or Annual
Specification Provisions
The amendment enables the Councils
to make changes to certain elements of
the SBRM through framework
adjustments and/or annual specification
packages rather than full FMP
amendments. All subject FMPs provide
for an efficient process to modify
aspects of the Northeast Region SBRM,
as relates to each specific FMP, should
the need arise and the appropriate
Council determine that a change to the
SBRM is warranted and needed to
address a contemporary management or
scientific issue. Depending on the
provisions of each FMP, changes to the
SBRM may be effected either through a
framework adjustment to the FMP or
through annual or periodic
specifications. Such changes to the
SBRM may include modifications to the
CV-based performance standard, the
means by which discard data are
collected/obtained in the fishery,
reporting on discards or the SBRM, or
the stratification (modes) used as the
basis for SBRM-related analyses. Such
changes may also include the
establishment of a requirement for
industry-funded observers and/or
observer set-aside provisions.
Prioritization Process
The amendment establishes a process
to provide the Councils and the public
with an opportunity to consider, and
provide input into, the decisions
regarding prioritization of at-sea
observer coverage allocations, if the
expected resources necessary may not
be available. In any year in which
external operational constraints would
prevent NMFS from fully implementing
the required at-sea observer coverage
levels, the Regional Administrator and
Science and Research Director will
consult with the Councils to determine
the most appropriate prioritization for
how the available resources should be
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allocated. In order to facilitate this
consultation, in these years, the
Regional Administrator and the Science
and Research Director will provide the
Councils, at the earliest practicable
opportunity: (1) The at-sea observer
coverage levels required to attain the
SBRM performance standard in each
applicable fishery; (2) the coverage
levels that would be available if the
resource shortfall were allocated
proportionately across all applicable
fisheries; (3) the coverage levels that
incorporate the recommended
prioritization; and (4) the rationale for
the recommended prioritization. The
recommended prioritization should be
based on: Meeting the data needs of
upcoming stock assessments; legal
mandates of the agency under other
applicable laws, such as the Marine
Mammal Protection Act (MMPA) and
the Endangered Species Act (ESA);
meeting the data needs of upcoming
fishery management actions, taking into
account the status of each fishery
resource; improving the quality of
discard data across all fishing modes;
and/or any other criteria identified by
NMFS and/or the Councils. The
Councils may choose to accept the
proposed observer coverage allocation
or to recommend revisions or additional
considerations for the prioritized
observer allocations ultimately adopted
and implemented by the Regional
Administrator and the Science and
Research Director.
Industry-Funded Observers and
Observer Set-Aside Program Provisions
The amendment implements
consistent, cross-cutting observer
service provider approval and
certification procedures and enables the
Councils to implement either a
requirement for industry-funded
observers and/or an observer set-aside
program through a framework
adjustment, rather than an FMP
amendment.
Comments and Responses
A total of 11 individual comment
letters were received on the proposed
rule and the amendment.
Comment 1: A letter by
representatives of a professional
association for at-sea fisheries observers
raised concerns regarding the provision
of the SBRM Amendment that
establishes observer certification and
approval procedures to allow a multiple
service delivery model under an
industry-funded observer program. The
commenters specifically focused on
concerns related to the contractual
relationship that would be established
between the observer service provider
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and the fishing vessel, rather than
between the observer service provider
and NMFS. The commenters refer to
experience with a similar model utilized
in Alaska under the North Pacific
Groundfish Observer Program. The
commenters cautioned that, in their
opinion, such a contractual relationship
may reduce the reliability of the data
collected by the at-sea observers due to
the potential for bias and conflict of
interest. The commenters also cited
concerns over quality control of the data
due to the lack of direct oversight by the
agency. To remedy the potential
problems they identified, the
commenters suggested that NMFS
evaluate the performance of approved
observer service providers on an annual
basis, increase Federal funding for
observers contracted by and paid for by
NMFS, and/or utilize an independent
non-profit organization (either an
existing organization such as the
Atlantic States Marine Fisheries
Commission or an organization created
specifically for this purpose) to provide
an ‘‘arms-length’’ relationship between
the fishing industry, NMFS, and
observer service providers.
Response: NMFS acknowledges that a
perceived conflict of interest could be a
potential issue for some types of
industry-funded observer programs.
Rigorous data quality assurance and
control standards, observer training and
certification programs, and frequent
reviews and oversight of the observer
data collection programs are all means
to address these concerns. NMFS
acknowledges that some of the issues
raised by the commenter regarding the
North Pacific Groundfish Observer
Program have been previously identified
as potential concerns with that model,
but notes that there are significant
differences between the North Pacific
program and the single industry-funded
program that is currently in place in the
Northeast Region. These differences
include the observer set-aside that is an
important component of the Northeast
sea scallop observer program and serves
to mitigate the conflict of interest
concerns by providing a mechanism to
offset the added cost to sea scallop
fishing vessels of carrying an observer.
Also, to minimize the likelihood that an
observer would develop ties to a vessel
owner/operator and/or feel pressure by
a vessel owner/operator to misreport,
the regulations prohibit observer service
providers from consecutively deploying
the same observer on the same vessel
and from deploying an observer on the
same vessel more than twice per month.
While NMFS shares some of the
concerns identified by the commenters
relative to the need to ensure that there
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is no real or perceived conflict of
interest between the at-sea observers
and the fishing vessels, and to ensure
reliable, high quality data are collected
and reported, none of these concerns are
immediately applicable to this
rulemaking. The regulatory changes
implemented in this final rule merely
establish the procedures that potential
observer service providers must follow
to be considered for approval, and the
standards that they must meet on a
continuing basis to maintain their
certification to serve in the Northeast
Region. However, excepting the sea
scallop observer program that was
formally implemented under a separate
rulemaking (72 FR 32549, June 13,
2007), no other fisheries in the
Northeast Region are operating under an
industry-funded observer requirement
that would utilize these regulations.
This action makes no changes to the
regulations or procedures established
under Amendment 13 to the Sea Scallop
FMP, other than to generalize the
observer certification procedures to
apply more broadly than for the sea
scallop fishery alone. The intent of this
action was to create a more efficient
process for the Councils to develop
future industry-funded programs,
should the need arise in any fishery.
Actual implementation of an industryfunded observer program that would
enable fishing vessels to select from a
list of approved observer service
providers would require the appropriate
Council to initiate, develop, and have
approved such a program for each
particular fishery.
The development of future Council
fishery management actions to
implement any additional industryfunded observer programs provides the
appropriate opportunity to ensure that
the programs fully address the data
quality concerns and limitations noted
by the commenters. NMFS is committed
to ensuring that data collected and
provided by at-sea fisheries observers
are of the highest-possible quality and
meet all applicable standards for
reliability, precision, and accuracy. Any
proposal by a Council to implement a
future industry-funded observer
program, such as is currently in place
for the sea scallop fishery, would be
reviewed to ensure it fully explains and
justifies how the data to be obtained
through the program meet all
appropriate quality standards.
Comment 2: One member of the
public endorsed the comments of the
observers’ professional association,
voicing his concern over industryfunded observer programs as exist in
Alaska under the North Pacific
Groundfish Observer Program. The
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commenter added, however, that his
concerns do not refer to the sea scallop
observer program that is linked to an
observer set-aside program to offset the
costs to the vessels of carrying an
observer. The commenter is most
concerned with the perceptions of
conflict of interest that can arise under
situations where the observer service
provider is contractually linked, and
dependent on, the fishing vessels rather
than NMFS.
Response: The response above to
comment 1 addresses the majority of the
points raised by the commenter. As
noted by the commenter, observer setaside programs, such as the Northeast
sea scallop program, mitigate many of
these concerns by providing a
mechanism to offset the added cost to
the vessel of carrying an observer. While
there is no requirement to do so, NMFS
fully anticipates that any program
developed by a Council to implement an
industry-funded observer program
would be directly associated with an
observer set-aside program that offsets
the additional costs to the vessels. No
such program is currently proposed or
under development by either Council,
but the SBRM Amendment provides a
mechanism for the Councils to develop
and propose a set-aside program that
uses quota, days-at-sea, increased trip
limits, or other means to compensate
fishing vessels that carry observers.
Comment 3: The comments submitted
by a public interest environmental
organization were very similar to those
of the observers’ professional
association. The commenters oppose
changing the NEFOP to a model based
on the North Pacific Groundfish
Observer Program, in which the
industry finances the observer program
through independent contracts with
observer service providers. The
commenters raised concerns regarding
the appearance of a conflict of interest
between the fishing vessels and the
observer service providers, a threat of
bias in the data collection, creating an
economic incentive to avoid
observation, less transparency of
observer data, and a lack of control on
harassment of an interference with
observers. The comment letter also
expressed concern that the SBRM would
discourage monitoring for marine
mammals and other non-bycatch related
monitoring.
Response: Although the commenters
in this case appear to have
misunderstood the intent of the SBRM
Amendment, NMFS takes their concerns
seriously. The response above to
comment 1 addresses the majority of the
concerns raised by the commenters, but
NMFS points out that the commenters
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claim that the SBRM Amendment
effects a ‘‘conversion’’ of the NEFOP
from one controlled by NMFS to an
industry-funded program. This is not
the case. The SBRM Amendment
provides a mechanism for the Councils
to develop and propose industry-funded
observer programs that would serve to
supplement the existing NMFS-funded
observer program, but this action
neither implements nor requires such a
program. Currently, the Councils are
free to develop and propose such a
system (as was done in Amendment 13
to the Sea Scallop FMP); the SBRM
Amendment allows the Councils to use
the framework adjustment process to
propose a similar program instead of
requiring a full FMP amendment. NMFS
fully anticipates that any such program
would include an observer set-aside
mechanism, such as exists for the sea
scallop fishery. As noted above and by
other commenters, such a mechanism
mitigates many of the concerns raised
by the commenters.
NMFS disagrees with the commenter
that such a system, should one be
proposed by a Council and
implemented by NMFS, would result in
industry ‘‘control’’ of the observer
program. The regulations at 50 CFR
648.11(h) and (i) provide extensive and
detailed procedures that must be
followed by all observer service
providers in order to obtain and
maintain NMFS certification as valid
service providers. These regulations
specifically address the issues of
potential conflicts of interest
(§ 648.11(h)(6)), harassment of or
interference with observers
(§ 648.11(h)(5)(vii)(F)), and data
transparency (§ 648.11(h)(5)(vii)(A)).
Regarding the concerns raised about the
availability of the ‘‘raw’’ observer data,
the regulations at § 648.11(h)(5)(vii)(A)
require that, in addition to providing
summary data within 12 hours of
landing, that the observer service
providers ‘‘provide the raw (unedited)
data collected by the observer to NMFS
within 72 hours of the trip landing.’’
Regarding the commenters’ opinion that
the plan creates an economic incentive
to evade observation, this claim does
not take into account that observer setaside programs in many ways may
actually create an incentive to be
observed, as a set-aside program would
grant a vessel extra quota, trips, DAS, or
increased possession limits in exchange
for carrying an observer.
The commenters are also incorrect
that the plan ‘‘discourages’’ marine
mammal monitoring. NMFS
acknowledges in the SBRM Amendment
the importance of its mandate under
other applicable laws, such as the
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MMPA and the Migratory Bird Act, but
the focus of the SBRM is on those living
marine resources defined as fish and
bycatch under the Magnuson-Stevens
Act. Only the Magnuson-Stevens Act
requires an SBRM to be established, and
the Magnuson-Stevens Act specifically
excludes certain types of organisms,
specifically marine mammals and birds,
from the definitions.
The commenters are mistaken to
conclude that the ‘‘SBRM is based on a
flawed model.’’ The actual SBRM
established as a result of this action is
wholly severable from the provision that
authorizes the Councils to develop and
propose an industry-funded observer
program through a framework
adjustment rather than an amendment
to an FMP. The SBRM does not
implement, require, or rely upon any
industry-funded observer programs that
may be developed and proposed by a
Council in the future.
Comment 4: An organization
representing a coalition of fishing
interests involved in the Atlantic
herring fishery submitted comments
critical of the field sampling protocols
and procedures used by at-sea observers
to monitor bycatch occurring in
fisheries that pump their catch directly
from the codend into the vessel hold.
The commenters asserted that the
current observer protocols for the
herring fishery contain loopholes that
were not addressed in the SBRM
Amendment, due to the potential for
unobserved catch to be released from
the net without being brought on board
the vessel for the observer to monitor.
The commenters expressed concern
regarding the lack of mandated observer
coverage on at-sea processing vessels,
which transfer catch from the codend of
catcher vessels to the hold of the
processor vessel and about how pair
trawls are treated if an observer is
aboard only one of the paired vessels.
The commenters also expressed concern
that the filtering procedures described
in the SBRM Amendment would result
in exclusion of certain fishing modes
(such as mid-water trawls) from
observer coverage due to low levels of
coverage in the past (‘‘the SBRM ensures
that [the mid-water trawl] mode will be
unobserved in perpetuity’’).
Response: All fishing vessels
permitted by NMFS to operate in the
Northeast Region under one or more of
the FMPs subject to the SBRM
Amendment are currently obligated to
carry a NMFS-certified observer on any
trip for which they are requested by the
Regional Administrator to do so (at
§ 648(a), (b), (c) , and (d)). This
requirement does not change, and is, in
fact, reinforced in section 1.7 of the
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amendment. This requirement, by
definition, applies to herring at-sea
processors. The commenters incorrectly
claim that the SBRM excludes some
fishing modes from observer coverage;
in fact, according to the results of the
importance filter adopted in the
amendment, the coverage allocated to
the New England mid-water trawl
fishing mode, cited by the commenters
as ‘‘unobserved in perpetuity,’’ would
be 316 days, nearly twice the coverage
level in 2004 and would represent 11.5
percent of trips taken in 2004. The
commenters appear to misunderstand
the function of the importance filters,
which is to eliminate certain species
(those for which the total discards in a
fishing mode is a negligible proportion
of either the total discards of that
species across all fishing modes, or for
which the total discards of that species
is a negligible proportion of total
fishing-related mortality of that species)
from the calculation of the observer
coverage allocation within a fishing
mode (the allocation being no less than
the highest coverage level of all species
remaining after the importance filter is
applied). Under no circumstances do
the importance filters eliminate any
fishing modes from the observer
allocation process. This can be seen in
Appendix C of the amendment in a table
illustrating the results of applying the
SBRM to the 2004 dataset. There is
some level of observer coverage
assigned to each of the 39 fishing modes
addressed in the SBRM Amendment. In
addition, the commenters asserted that
the SBRM Amendment did not address
the field sampling protocols to be used
in collecting data by at-sea fisheries
observers. This is incorrect. Section 1.7
of the SBRM Amendment stipulates that
‘‘The NEFOP shall serve as the primary
mechanism to obtain data on discards in
all Northeast Region commercial
fisheries managed under one or more of
the subject FMPs,’’ and that ‘‘all data
obtained by the NEFOP under this
SBRM shall be collected according to
the techniques and protocols
established and detailed in the Fisheries
Observer Program Manual (NEFOP
2006a) and the Biological Sampling
Manual (NEFOP 2006b).’’ This section
of the SBRM Amendment goes on to
identify the minimum data fields to be
collected by Northeast Region observers.
The Fisheries Observer Program Manual
and the Biological Sampling Manual
provide general as well as specific
instructions for at-sea observers
operating on mid-water trawl, purse
seine, and pair trawl vessels; these
instructions and sampling priorities
explicitly account, to the extent
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practicable, for the contingencies
identified by the commenters (including
pair trawls with only one vessel
observed, pumped fish, loss of fish in
the net, etc.).
Comment 5: A letter from an
organization representing commercial
fishermen from Cape Cod expressed
concern with how the SBRM would
perform in monitoring hard TACs (total
allowable catch) and fishery sectors.
The commenters acknowledged that at
least some of the changes under the
SBRM Amendment will improve the
region’s bycatch reporting, and
characterized the importance filter
process as ‘‘crucial for prioritizing
observer coverage.’’ However, the
commenters stressed three primary
recommendations for improving the
SBRM Amendment: (1) Ensuring that
the SBRM provides a means to
accurately and precisely quantify
discards for all stocks across all stock
areas; (2) identifying levels of
monitoring coverage for sectors
necessary for TAC management; and (3)
providing a real-time, publiclyaccessible, and transparent reporting
methodology that allows for
enforcement of accountability measures.
Response: The commenters imply that
the SBRM Amendment should have
addressed the new requirement
included in the Magnuson-Stevens
Reauthorization Act of 2007 (MSRA) for
all FMPs to include ‘‘Annual Catch
Limits’’ (ACLs) and ‘‘Accountability
Measures’’ (AMs) and indicate how the
SBRM would perform in the face of
these new requirements. However, the
MSRA does not require ACLs and AMs
be developed and implemented for any
fishery until at least 2010 (for fisheries
experiencing overfishing) or 2011 (for
all other fisheries). Also, the new MSRA
provision related to ACLs and AMs, by
its very definition, applies to all catch,
not just bycatch, and is a requirement
much broader in scope than the
requirement to establish an SBRM,
which remains a separate requirement
under the Magnuson-Stevens Act and
was not modified by the MSRA. Section
1.2 of the SBRM Amendment
acknowledges the changes promulgated
through the MSRA, but explains that no
changes to the amendment are necessary
as a result. This action remains
necessary primarily to correct
deficiencies identified by the Court in
Amendment 13 to the Northeast
Multispecies FMP and Amendment 10
to the Sea Scallop FMP in order to bring
the Northeast Region FMPs into
compliance with the requirement to
establish an SBRM as specified as
section 303(a)(11) of the MagnusonStevens Act. As the Councils embark on
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fishery management actions to bring the
FMPs into compliance with the new
requirements of the MSRA, changes to
the SBRM established herein may be
necessary to accommodate the specific
attributes of the ACLs and AMs that will
be developed, but such changes would
address specific management needs that
go beyond the mandate of section
303(a)(11) to establish an SBRM to
assess the amount and type of bycatch,
which is the focus of this action.
Because it is impossible at this time to
foresee all the particular attributes of the
various ACL and AM programs that may
be developed and adopted by the two
Councils for all 13 FMPs, and how the
SBRM may need to change to
accommodate those programs, it would
be premature to attempt to craft an
SBRM that could accommodate all
possible ACL and AM outcomes,
without resulting in an SBRM so vague
and generalized as to be ineffectual at
meeting its current objectives.
Regarding the specific points raised
by the commenter, NMFS asserts that
the Northeast Region SBRM is wholly
sufficient to quantify discards for all
stocks across all stock areas. Data
collected by at-sea fisheries observers
provide sufficient information to
determine the specific stocks of fish
discarded, and the stock areas in which
the discard event occurred. These data
can be used to apportion the collected
discard estimates across all stocks and
stock areas. This is illustrated in
Appendix F and Appendix G of the
amendment, which provide example
data queries and analyses based on the
data collected by at-sea observers and a
sample format for the information
requested by the Councils to be
provided in annual discard reports. In
both cases, discard data are summarized
by stock and statistical area, which is a
finer scale even than stock area (i.e.,
stock areas are composed of multiple
statistical areas).
The commenters also suggest that the
SBRM must identify observer coverage
levels for fishery sectors authorized
under an FMP to provide for a specific
level of certainty in future TAC
management programs. The commenters
appear to assume that a one-size-fits-all
approach would be appropriate for all
potential future instances of sector
management. Sectors are unique and
temporary fishery management
provisions that authorize a collective of
similar fishing vessels (e.g., hook vessels
operating out of Cape Cod) to be granted
a portion of a TAC for 1 year in
exchange for abiding by the specific
provisions and limitations identified in
the sector management plan. Currently,
there are two approved sectors operating
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4741
in New England waters; both are
authorized under the sector
management provisions of Amendment
13 to the Northeast Multispecies FMP.
As many as 19 additional multispecies
sectors are under development, and the
New England Council is considering
adopting similar sector provisions in
upcoming amendments to the other
New England FMPs. The sector
provisions of the Northeast Multispecies
FMP require that the vessels interested
in forming a sector prepare and submit
annually a sector proposal that includes,
among other things, ‘‘detailed plans for
the monitoring and reporting of
landings and discards’’ (at
§ 648.87(b)(2)(vi)). Under the sector
provisions of the FMP, it is the
responsibility of the sector proponents
to propose how discards will be
monitored and reported, while the
Council and NMFS retain the authority
to determine if the proposed plans are
sufficient. Sector proposals developed
by members of the fishing industry are
submitted to and reviewed by the New
England Council. Those approved by
the Council are incorporated into
framework adjustments to the Northeast
Multispecies FMP and submitted to
NMFS for review. At that time, NMFS
considers the specific provisions of the
proposed sector plan to ensure it would
meet all requirements of the FMP and be
consistent with the provisions of the
Magnuson-Stevens Act and other
applicable law. Given the variety of
sector proposals currently under
development, and the expectation of
additional sector provisions included in
the other New England FMPs, it would
not be practicable to stipulate in this
amendment the specific levels of
observer coverage that would be
necessary for each sector, as this would
depend on the number of vessels
participating, the area(s) to be fished,
the target and likely incidental species,
fishing gear(s) used, and the other
reporting mechanisms required under
each sector plan. This action is focused
on the requirement at section 303(a)(11)
of the Magnuson-Stevens Act to develop
a methodology to assess the amount and
type of bycatch and provides a
framework for modifications to the
overarching methodology to address
specific future management needs. The
Councils recognized the need for the
SBRM Amendment to be flexible
enough to adapt to such changes, noting
in section 6.9.5 of the amendment that
because new sector programs may be
implemented through a framework
adjustment, the same framework action
could be used to ‘‘modify the SBRM to
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ensure sufficient data are collected’’ on
discards.
The commenters asserted that the
SBRM must establish a ‘‘real-time,
publicly-accessible, and transparent
reporting methodology.’’ NMFS
disagrees with the commenters on this
point. The Magnuson-Stevens Act
requires simply that an SBRM be
established; it imposes no minimum
legal requirements on whether this
system provide data in real time, or the
degree to which the data are publicly
accessible. A ‘‘real-time’’ reporting
system, as requested by the commenters,
would require that data be presented in
a publicly accessible medium as the
discards are observed and documented
by the at-sea fisheries observer. This
would provide no time for the fishing
trip to end, for the observer to submit
the data to NMFS, and for NMFS to
review, edit, and audit the data prior to
publishing the data. This would
severely reduce the quality of the data
and, in so doing, diminish the
usefulness and reliability of the discard
data. Data reduction and summaries are
necessary in order to prevent the release
of sensitive and proprietary data that is
protected under the Magnuson-Stevens
Act and other Federal statutes. NMFS
concludes that it is more appropriate to
engage a full data quality control and
assurance program, as summarized in
Appendix D of the SBRM Amendment,
in order to ensure the resulting data are
of the highest possible quality before
they are released to the public or used
in management.
Comment 6: A conservation
organization submitted extensive
comments on the SBRM Amendment
and its proposed rule, urging that NMFS
not approve the amendment. The
comments addressed several elements of
the SBRM Amendment, and include
references to the results of a technical
review of the amendment conducted
under contract to another conservation
organization. The responses to the
comments identified in the technical
review are addressed separately under
comment 10. All other points raised in
the comment letter are addressed in this
response.
The commenters, while
acknowledging that the SBRM
Amendment ‘‘dramatically’’ improves
upon prior documents by specifying a
monitoring and reporting system that
could be implemented, expressed
concern that the amendment fails to
actually establish this system because it
vests NMFS with discretion as to the
allocation of observer coverage if there
are external constraints (such as an
insufficient budget) that prevent full
implementation. The commenters
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suggested that the amendment could
have adopted a formal decision
procedure that would stipulate how
observers are to be allocated if there is
a budget shortfall, such as requiring that
the budget allocations be cut pro rata
across all fishing modes, or to rank
fishing modes according to a standard of
priority and fully allocating observer
coverage across priority modes until
funding is exhausted.
The commenters claim that the SBRM
Amendment fails to mandate that data
be reported in a rational manner useful
for fisheries management, and that the
amendment fails to establish a reporting
requirement that provides information
on the amount, type, and disposition of
bycatch. The commenters also claim
that the amendment fails to recognize
the fishery management needs of the
Councils and the needs of the public.
The commenters claim that the
amendment fails to establish an SBRM
because it provides for framework
adjustment provisions to enable the
Councils to develop and propose
changes to the SBRM. The commenters
also claim that the SBRM Amendment
fails to consider the bycatch of species
that are not targeted under Northeast
Region FMPs, including failing to
consider alternatives for including
‘‘non-managed’’ species in the SBRM.
The commenters claim that NMFS
‘‘locked’’ the public and Fishery
Management Councils out of the
decision-making process to develop the
SBRM Amendment. The commenters
also claim that the SBRM Amendment
violates NEPA because an
environmental impact statement (EIS)
was not prepared. Regarding the
environmental assessment’s (EA)
compliance with NEPA, the commenters
raised the following concerns: The EA
fails to adequately discuss the purpose,
need, and scope of the amendment; the
EA fails to consider a reasonable range
of alternatives, including performance
standards other than 30 percent,
different reporting formats or
frequencies, or different ways to assess
accuracy; the EA fails to consider
cumulative environmental impacts; and
the EA fails to adequately address
protected resources.
Response: NMFS disagrees with the
commenters’ assertion that the
amendment fails to establish an SBRM
because it vests NMFS with some degree
of discretion in cases where external
operational constraints prevent full
implementation of the resulting at-sea
observer allocations. The SBRM
Amendment establishes an extensive
and detailed methodology to utilize
available observer data on discards
occurring across all relevant Northeast
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Region fisheries, assess the degree to
which those data meet the established
performance standard, allocate observer
coverage levels across all relevant
fisheries to achieve said performance
standard, and provide reports to the
Fishery Management Councils on the
discards that are occurring and on the
effectiveness of the SBRM itself at
meeting its objectives. The prioritization
process is one component of the overall
program that explicitly recognizes that
external operational constraints (such as
Congressional budget allocations) may
occasionally prevent the full
implementation of the SBRM. The
process establishes a rigorous review
and consultation process to engage the
Councils and the public in determining
the most appropriate approach to
prioritize observer coverage on these
occasions that reflects the needs and
priorities of the agency and Councils at
the time.
The commenters suggested that the
amendment could have implemented a
requirement to apportion any budget
allocations pro rata across all fishing
modes, or could have ranked fishing
modes according to a specific standard
of priority and require that observers be
fully allocated to the highest priority
modes in descending order until the
available budget is exhausted. NMFS
notes that several options such as these
are described in section 6.6 of the
amendment, but that the Councils
recognized the importance of retaining
sufficient flexibility in the SBRM to
adapt to changing conditions and
priorities in the fisheries. The approach
suggested by the commenters would
leave the Councils and NMFS with a
rigid system that would require an FMP
amendment to modify the priority
allocation of resources. NMFS also notes
that retaining some level of discretion in
allocating resources is necessary for the
agency to adequately meet its
obligations under other laws in addition
to the Magnuson-Stevens Act, such as
the ESA and MMPA. Lastly, the
commenters appeared to have
misconstrued the instructions from the
Court. Instead of requiring that the
SBRM Amendment stipulate the precise
areas where observers must be
concentrated, the Court, in Oceana II,
clarified that it ‘‘only requires that the
FMP establish some method for
determining observer concentration
instead of leaving all decisions to the
Regional Administrator’s discretion’’
[See, Oceana II at p. 234 (footnote 41)].
The SBRM Amendment establishes a
very specific method for determining
observer allocations across all relevant
fisheries, and does not leave ‘‘all
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decisions’’ to the Regional
Administrator. Rather, only in years in
which external operational constraints
prevent full implementation would
NMFS have any discretion to adapt the
results of the SBRM, and only then
following a review and consultation
with the Councils in a public forum.
NMFS asserts that this approach is
consistent with both the intent of the
SBRM provisions of the MagnusonStevens Act and the guidance provided
by the Court.
NMFS rejects the commenters’ claim
that the SBRM Amendment fails to
mandate that data be reported in a
rational manner useful for fisheries
management, and that the amendment
fails to establish a reporting requirement
that provides information on the
amount, type, and disposition of
bycatch. Section 6.4 of the SBRM
Amendment describes the alternatives
considered regarding potential reporting
procedures, and section 1.7 of the
amendment establishes the
requirements for two types of reports to
be prepared at different time intervals.
The amendment requires an annual
report be provided to the Councils to
provide the data they requested on the
current status of observer coverage and
discard information, along with an
additional report provided every 3 years
that assesses the SBRM in a more
comprehensive manner. The
amendment, in sections 1.7 and 6.4,
identifies the specific data elements to
be provided in the reports, including the
amount, species, location, and gear
types involved. The information to be
reported, the frequency, and the format
for the reports was proposed and
adopted by both Councils as their
preferred alternative approach to
obtaining SBRM reports on a routine
basis. NMFS asserts that the Councils
are in the best position to determine
their needs as to SBRM reports, and, as
such, the SBRM Amendment clearly
reflects the needs of the Councils for
this information.
NMFS disagrees with the commenters
that the SBRM Amendment fails to
actually establish an SBRM simply
because it provides a procedure for the
Councils to make changes to certain
provisions of the SBRM through the use
of framework adjustments rather than
full FMP amendments. The intent of
this provision of the amendment is to
facilitate an efficient and timely process
for the Councils to develop and submit
proposed changes to the SBRM, limited
within certain constraints. Nothing in
this provision diminishes or abrogates
the agency’s obligation to carefully
review any framework adjustment
proposed by a Council to ensure that the
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proposed changes are consistent with
the Magnuson-Stevens Act, other
applicable law, and do not undermine
or contravene the parent FMP. The
amendment clearly stipulates that
intent, as at section 6.5.2, which
provides that ‘‘the intent of this
[framework] provision is to provide an
efficient means for the Council to
change the performance standard in
certain circumstances when a higher
level of precision (i.e., reducing the CV
to less than 30 percent) is desired for a
particular fishery or management
program [emphasis added].’’ Providing
this mechanism to modify certain
elements of the SBRM is considered
important because several provisions of
the parent FMPs already establish
framework adjustment protocols for
items such as creating new special
access programs (SAPs) or new fishery
sectors. As these changes are developed
through a framework adjustment
process, changes to the SBRM may be
necessary in order to ensure sufficient
discard reporting in the new SAP or
sector. Without the ability to effect the
necessary changes to the SBRM through
the framework adjustment
implementing the SAP or sector, the
Council would have to defer
implementation of each such framework
until an accompanying amendment
could be developed to implement the
changes to the SBRM. This delay would
directly contravene the intent of the
parent FMPs.
NMFS also disagrees with the
commenters that the amendment failed
to consider the bycatch of species that
are not targeted under the Northeast
Region FMPs. This issue is addressed in
several sections of the amendment.
First, section 1.7 of the amendment
clearly stipulates that the data collected
by at-sea fisheries observers ‘‘shall be
collected on all species of biological
organisms caught by the fishing vessel
and brought on board, including species
managed under the subject FMPs but
also including species on non-managed
fish, invertebrates, and marine plants.’’
This section of the amendment
continues to stipulate, in a footnote, that
a complete list of the species for which
the listed data elements are to be
collected can be found in Appendix A
and Appendix R of the Fisheries
Observer Program Manual. These lists
include more than 500 distinct species
and species codes that must be
accounted for by observers in their catch
and discard reports. This provision of
the SBRM requires that information
regarding the discards of all species be
reported by at-sea observers and
reported to NMFS. The same
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information collected on species
managed under a subject Northeast
Region FMP would also be available, at
the same level of detail, on all other
species. The SBRM, however, is
specifically crafted around the species
managed under a subject FMP, and it is
these species, with the addition of
threatened and endangered sea turtles,
that drive the allocation of observers
across the subject fishing modes.
Contrary to the claim of the
commenters, the Councils explicitly
considered expanding this aspect of the
SBRM calculations to include all nonmanaged species. This is described in
section 6.8.1 of the amendment
document and includes the Councils’
rationale for not so expanding the
SBRM.
NMFS rejects the claim by the
commenters that the agency ‘‘locked’’
the public and Councils out of the
decision-making process to develop the
SBRM Amendment. The process to
development the amendment included
numerous and varied opportunities for
the public and the Councils to fully
engage and provide valued input,
fulfilling the letter and spirit of NEPA.
The commenters correctly pointed out
that the primary analyses and technical
materials were developed by a Fishery
Management Action Team (FMAT) that
was chaired by a NMFS staff member,
but claim that this represents a ‘‘flawed’’
approach. The choice of a NMFS staff
member to serve as chair of this
technical group was suggested by the
Councils as a way to help with staffing
resource concerns shared by the
Councils. However, in all respects other
than the position of the group’s chair,
the membership of the FMAT reflected
the standard operating procedures for
Plan Development Teams (PDTs), as
used by the New England Council, as
well as FMATs as used by the MidAtlantic Council. The SBRM FMAT
included staff from both Councils, the
Northeast Fisheries Science Center,
NOAA General Counsel, and the
Northeast Regional Office, all with the
requisite expertise and background in
the subject matter.
All activities, analyses, and
recommendations of the FMAT were
reported to a Joint Oversight Committee
composed of voting member of both
Councils, and all such meetings of the
SBRM Committee were held in public
fora with advance notice to the public.
Throughout the development of the
amendment, the SBRM Committee held
six public meetings ranging in location
from Virginia Beach, VA, to Peabody,
MA. All decisions of the Councils with
regards to establishing the range of
alternatives to be considered in the
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amendment, selecting the preferred
alternatives, approval of the draft
amendment for release to the public,
reviewing the results of the analyses and
information provided by the FMAT,
assessing the comments submitted by
the public on the draft amendment and
the changes proposed to address those
comments were first vetted through the
SBRM Committee in public meetings. In
addition to the six meetings of the
SBRM Committee, the Councils met
publicly a total of 13 times to receive
reports on the progress of the SBRM
Amendment, to review the decisions
and recommendations of the SBRM
Committee, and to formally approve and
adopt the amendment for release to the
public and, later, to submit for
Secretarial review. There was also a
public meeting at which members of
both Councils’ SSCs conducted a formal
peer-review of the technical
components of the SBRM Amendment,
and two public hearings were held to
provide ample opportunity for
interested members of the public to
provide comments on the draft
amendment.
Lastly, NMFS disagrees with the
assertion by the commenters that the
SBRM Amendment violates NEPA
because an EIS was not prepared.
Consistent with NEPA, Council for
Environmental Quality (CEQ)
regulations, and NOAA administrative
policy, NMFS and the Councils
collaborated to prepare an EA to
evaluate the significance of the
environmental impacts expected as a
result of the actions considered in the
SBRM Amendment. The results of this
assessment are provided in section 8.9.2
of the amendment, which supports the
finding of no significant impacts
(FONSI) signed by the agency on
October 16, 2007. The commenters
provided no evidence, nor even any
claims, that the conclusions in the
FONSI are not supported by the facts
presented in the EA for this finding.
Contrary to the claim of the
commenters, NMFS asserts that the EA
considers a sufficient range of
alternatives to satisfy the requirements
of NEPA. As described throughout the
amendment (the Executive Summary
and chapters 6, 7, and 8), the
alternatives considered by the Councils
were structured around seven specific
elements that together comprise the
Northeast Region SBRM. Multiple
alternatives were developed and
considered for each element and, in
some cases, various sub-options were
also developed and considered. As
noted in Appendix E of the amendment,
in response to a similar comment
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received on the draft amendment, the
available permutations of the various
alternatives considered in this action
exceeds 1,400 if the sub-options are not
counted. Accounting for the suboptions, the number of possible
outcomes exceeds 2,100 distinct sets of
management alternatives. In addition to
the sets of alternatives expressly
analyzed in the EA, the Councils
considered, but ultimately rejected from
detailed analysis, an additional four
distinct alternatives. These additional
alternatives are described in section 6.8
of the amendment, and, contrary to the
claim of the commenters, include
alternatives that specifically addresses
setting alternate CV levels and different
intervals for the SBRM reports.
NMFS disagrees with the commenters
that the EA fails to adequately discuss
the purpose, need, and scope of the
amendment. All of these elements are
specifically identified and are fully
described in chapter 1 of the
amendment. The commenters assert that
the EA fails to consider cumulative
environmental impacts. NMFS rejects
this claim, as section 7.3 of the
amendment explicitly provides a
discussion of the expected cumulative
effects associated with the action. NMFS
asserts that this treatment of cumulative
effects is consistent with CEQ
regulations and current NOAA policy.
Regarding protected resources, several
elements of sections 7.1 and 7.2 of the
amendment address the potential
impacts of the actions on protected
resources, and NMFS considers this
treatment, along with sections 8.3 and
8.8 of the amendment, to be adequate
under all applicable law. Endangered
sea turtles are explicitly addressed in
the SBRM (see chapters 5 and 6), and
are afforded a priority superior to all
other fish species by ‘‘trumping’’ the
second and third level importance
filters (i.e., if the results of the second
and third level importance filters would
result in an observer allocation to a
fishing mode that is less than the
number of sea days calculated to
adequately observe sea turtles, then the
higher sea turtle allocation is applied).
As noted throughout the amendment
document, the Magnuson-Stevens Act
specifically excludes marine mammals
and birds from the definitions of fish
and bycatch and, therefore, the SBRM
(because it exists solely as a MagnusonStevens Act construct) need not
expressly account for marine mammals
or birds. Therefore, NMFS considers the
SBRM Amendment to adequately
address protected resources.
Comment 7: A comment letter written
on behalf of four conservation
organizations raised many of the same
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concerns as the conservation
organization noted above. In particular,
the commenters frequently referred to
the results of the technical review
described below. The responses to the
comments identified in the technical
review are addressed separately under
comment 10. All other points raised in
the comment letter are addressed in this
response.
The commenters claim that the SBRM
Amendment fails to achieve the purpose
of the action or meet the related
requirements of the Magnuson-Stevens
Act and the prior Court orders because
it fails to explain the methods and
processes by which bycatch is currently
monitored, fails to determine whether
these methods and process should be
modified and/or supplemented, and
fails to document the SBRM established
for all Northeast Region FMP fisheries.
The commenters claim that the SBRM
Amendment does not explain the
methods by which data and information
on discards are obtained by observers.
The commenters reiterated the claim
made in comment 4 that the SBRM
Amendment ‘‘conclude[s] that observer
coverage is not warranted’’ in the midwater trawl fishery.
The commenters claim that the SBRM
Amendment fails to specify levels of
observer coverage required for each
FMP, citing concern that the ‘‘mere
performance targets’’ leave the actual
level of observer coverage entirely up to
the agency. The commenters also claim
that the SBRM fails to adequately cover
‘‘non-managed’’ bycatch species.
The commenters claim that NMFS
‘‘prevented’’ the New England and MidAtlantic Councils and the public from
meaningfully participating in the
development of the SBRM Amendment.
Similar to the previous commenter, the
commenters claim that an EIS should
have been prepared, rather than the EA,
and that the document therefore does
not comply with NEPA. In particular,
the commenters claim that the lack of an
EIS: Limited the opportunities for
public participation and stymied the
involvement of the Councils; failed to
consider a range of alternatives; and
failed to ensure that decision-makers
and the public are well informed about
the potential environmental impacts of
the action. The commenters suggested
that the amendment should have been
presented in a more accessible format,
claiming that the SBRM is a ‘‘nearly
incoherent document.’’ The commenters
claim that the FMAT formed to prepare
the technical materials for the Councils
was a ‘‘failure’’ and failed to engage the
Councils. The commenters further claim
that the SBRM Amendment was
‘‘carefully steered around the avoidance
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of the public participation requirements
of NEPA,’’ and that opportunities for
public participation, including the two
public hearings, were limited to Council
meetings with short agenda items and
‘‘little or no’’ opportunity for public
comment. The commenters also
criticized the amount of time available
to review and comment on the
amendment, claiming that much of the
document was not available ‘‘in any
form’’ until shortly before the Councils
approved the document in June 2007.
The commenters concluded by
criticizing the 60-day comment period
on the amendment, claiming that this
amount of time was insufficient.
The commenters suggested that NMFS
engage independent and objective
scientific expertise, along with the
public, and prepare an EIS in support of
a ‘‘significantly revised’’ SBRM
Amendment. The commenters claim
that the SBRM was never peer reviewed
by independent reviewers at any stage
of its development. The commenters
recognized that the document was
reviewed by members of the Councils’
SSCs, but claim that these reviewers
‘‘lacked the highly specialized expertise
necessary to conduct a review of this
nature,’’ and that the reviewers cannot
be considered as independent and
objective because they serve as members
of the Councils’ SSCs.
Response: NMFS disagrees that the
amendment fails to explain the methods
and processes by which bycatch is
currently monitored or that the
amendment fails to evaluate whether
these methods should be modified and/
or supplemented, noting that chapter 4
addresses these specific issues.
Additional information about the
current bycatch data collection
programs is provided in chapter 5 of the
amendment and in associated reference
documents that are clearly identified
throughout the amendment. As noted
above in response to comments on this
issue, it is incorrect to conclude that the
SBRM Amendment in any way suggests
that observer coverage ‘‘is not
warranted’’ in any fishing mode,
including the New England mid-water
trawl mode, which the amendment
indicates would be allocated 316
observer sea days based on the 2004
observer data, a two-fold increase over
the actual coverage in this fishing mode
in 2004.
NMFS disagrees with the
commenters’ implication that the SBRM
Amendment was intended to specify
levels of observer coverage required for
each FMP. Nothing in the MagnusonStevens Act, or in either relevant Court
order described above, requires that an
SBRM include specific observer
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coverage levels to be identified for each
FMP. Rather, the intent of the
Magnuson-Stevens Act SBRM provision,
supported by the Court, was to establish
procedures to determine the appropriate
levels of coverage [See, Oceana II at p.
233 (footnote 38), where the Court states
that ‘‘Oceana I did not require that an
FMP mandate a specific level of
observer coverage’’]. The amendment
clearly establishes the procedures to be
used to make these determinations and
requires that the agency utilize these
procedures (‘‘Each year, the Regional
Administrator and the Science and
Research Director shall allocate
sufficient at-sea observer coverage to the
applicable fisheries of the Northeast
Region in order to achieve a level of
precision . . . no greater than 30 percent
for each applicable species and/or
species group’’ SBRM Amendment at
section 1.7).
The commenters’ claim that the
agency ‘‘prevented’’ the Councils from
participating in a meaningful way in the
development of the amendment is
patently false. As described earlier in
response to previous comments, the
development of the SBRM Amendment
was conducted under the oversight of a
joint Council committee that included
members from both Councils. All
decisions regarding the development of
the amendment were made by the
Councils and were based on the
recommendations of the SBRM
Oversight Committee. Contrary to the
claim of the commenters, the evidence
clearly indicates that both Councils
were fully engaged in the development
of this amendment, and there were no
actions taken on the part of the agency
to ‘‘prevent’’ such engagement.
NMFS considers the SBRM
Amendment and associated EA to
comply fully with the requirements of
NEPA, the CEQ regulations, and NOAA
Administrative Order 216–6, and,
therefore, rejects the assertion by the
commenters that an EIS should have
been prepared. According to the CEQ
regulations, and all available guidance
on the subject, an EIS need only be
prepared when an EA or other related
analysis identifies significant effects on
the environment or if the facts available
to the action agency cannot support the
conclusions required in order to make a
FONSI. The EA associated with the
SBRM Amendment fully evaluated the
expected direct, indirect, and
cumulative impacts likely to result from
implementation of the action. The EA,
in both form and scope, followed all
agency guidelines for an EA associated
with an FMP amendment. As noted in
response to previous comments, a full
range of reasonable alternatives was
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considered by the Councils during the
development of the amendment, and all
relevant effects of the action, and its
alternatives, were identified and made
available to the relevant decisionmakers. In response to the claim that the
amendment document is ‘‘nearly
incoherent,’’ NMFS notes that at no
stage in the development of the
amendment did anyone else raise such
a comment. NMFS considers this
amendment to be an organized, wellwritten, and approachable document
that includes each element required by
NEPA and all applicable laws. The
inclusion in the amendment of highly
technical concepts and methodologies
was necessary in order to treat the
statistical analyses and modeling
elements inherent in the development of
an SBRM in a complete and transparent
manner. Great care was taken to present
this information clearly, to organize the
amendment in a logical manner, and to
use clear prose to the extent possible.
NMFS disagrees with the claim that
the FMAT process was a failure. The
FMAT members included
representatives from both Councils’
staffs, and the FMAT reported to the
Councils’ SBRM Oversight Committee at
each step in the process to develop the
amendment. The FMAT produced a
draft amendment 8 months after the first
FMAT meeting, at which time it was
accepted by both Councils and released
for public review. Following the public
comment period on the draft
amendment and draft EA, the FMAT
prepared revisions to several sections of
the amendment and presented all
revisions to the Committee less than 4
months after the end of the comment
period. NMFS considers the FMAT
process to be a success by all accepted
standards and practices for Council
actions. Regarding the claim that the
development of the amendment was
intended to avoid public participation,
as noted above in response to the
previous comment on this issue, public
participation was encouraged and
multiple opportunities for public
participation were provided throughout
the development process. Both public
hearings held on the draft amendment
were noticed well in advance of the
hearings, both were held in public
venues in conjunction with, but not
during, public meetings of the New
England and Mid-Atlantic Councils.
Both hearings were relatively well
attended (32 individuals attended the
first hearing in Gloucester, MA, and 16
individuals attended the second hearing
in New York, NY), and both hearings
remained open until all in the audience
who wished to provide comment had
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done so. No time limits were placed on
any commenter, and no one was
precluded from speaking. As a result of
the discussions of the Councils and
comments from the public, several
changes to the SBRM Amendment were
made throughout its development,
including the revisions to the
importance filter process, the inclusion
of multiple reporting procedures, and
the incorporation of an external peer
review of the underlying analyses
conducted by the Councils’ SSCs.
NMFS disagrees with the claim of the
commenters that the document was not
available ‘‘in any form’’ until shortly
before the Councils approved the
document in June 2007. Drafts of the
amendment and EA were available prior
to the Council meetings in September
and October 2006 at which the draft
amendment was approved for release to
the public for public hearings. The
public hearing draft of the amendment
and EA was posted to the Internet and
made available on November 1, 2006,
initiating a 60-day comment period.
Copies of the public hearing draft were
available by mail for anyone who
requested one, and copies were
available at both public hearings. The
public hearing draft of the amendment
and EA remained available on the
Internet until it was replaced by a
revised draft in mid–2007. In advance of
the April 2007 meeting of the SBRM
Oversight Committee, errata sheets
reflecting the sections of the draft
amendment that had been revised to
address public comments were made
available on the New England Council’s
Internet page. Copies of these revised
sections of the amendment were also
made available at the April 2007
meeting. Following the April 2007
meeting of the Committee, these revised
sections were integrated into the draft
amendment, and a final draft of the
amendment was posted to the Internet
in early June.
Regarding the criticism that the 60day comment period on the amendment
(72 FR 41047) was insufficient, NMFS
notes that this 60-day time period for
public review of FMPs and amendments
is stipulated in section 304 of the
Magnuson-Stevens Act (‘‘Upon
transmittal by the Council to the
Secretary of a fishery management plan
or plan amendment, the Secretary shall
. . . immediately publish in the Federal
Register a notice stating that the plan or
amendment is available and that written
information, views, or comments of
interested persons on the plan or
amendment may be submitted to the
Secretary during the 60-day period
beginning on the date the notice is
published.’’).
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NMFS asserts that it is unnecessary to
engage additional expertise, and finds
no reason to disapprove and revise the
SBRM Amendment. NMFS disputes the
commenters’ claim that the SBRM was
not peer reviewed by independent
reviewers, noting that both Councils
solicited their respective SSCs for
members with the expertise to conduct
a formal peer review of the technical
components of the SBRM Amendment.
Four reviewers, two from each Council’s
SSC, with all the requisite expertise and
background to conduct such a review,
met in August 2006 in a public forum
to assess the SBRM. The results of the
peer review were made publicly
available in September 2006 and were
fully addressed in revisions to the initial
draft of the SBRM Amendment and all
comments and suggestions made by the
SSC members were incorporated.
Comment 8: A comment letter by the
chief scientist for a conservation
organization asserted that the analyses
and preferred options in the SBRM
Amendment represent improvements
over previous versions. The commenter
stressed that the selected alternative for
the importance filter is ‘‘much better’’
than the non-preferred alternative, and
that it is ‘‘appropriate’’ to concentrate
observer sampling effort on fishing
modes that cause a high fraction of the
discard mortality and a high fraction of
the total fishing mortality for each
harvested species. The commenter also
stated that the preferred alternative
precision standard (a CV of 30 percent)
for bycatch estimates for each managed
species and fishing mode is
‘‘appropriate.’’ In addition, the
commenter concurred with one of the
conclusions of the McAllister report (see
below) that simulation testing should be
done to evaluate the precision and
potential biases of each proposed
estimator.
Response: NMFS agrees with the
commenter that the SBRM represents an
improvement over previous versions,
that the importance filter is a sound and
appropriate approach to concentrate
observer coverage, and that the
performance standard of a 30 percent
CV is appropriate for discard estimates.
The response to the comment
concurring with the McAllister report
on simulation testing is addressed
below in response to comment 10.
Comment 9: A comment letter written
by attorneys representing an association
of full-time, limited access scallop
fishermen in New England and the MidAtlantic endorsed the SBRM
Amendment, noting that, in their
opinion, the SBRM Amendment
addresses all relevant legal
requirements. The commenters claim
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that the amendment establishes an
appropriately flexible system to meet
unknown future demands on the
observer system. The commenters assert
that the amendment appears to have
achieved a reasonable and practicable
balance in the scope of the SBRM and
the approach taken to allocate observer
coverage across the subject fishing
modes. The commenters support the use
of the importance filters by focusing
limited resources on the areas of greatest
concern to management. The
commenters also support the provisions
of the rule that allows the Councils to
develop an observer set-aside program
through a framework adjustment to the
FMP, rather than a full amendment. In
addition, the commenters support the
establishment of standards for certifying
additional observer service providers.
Response: NMFS agrees with the
comments.
Comment 10: A comment letter from
a conservation organization included a
detailed technical review of the
scientific analyses and methodology
underlying the SBRM Amendment. A
technical review was submitted by Dr.
Murdoch McAllister of the University of
British Columbia. Although the
McAllister report found the importance
filters to be ‘‘scientifically sound,’’
‘‘well-founded,’’ and ‘‘sensible from a
scientific point of view’’ and to be
effective at reducing the amount of
observer effort required without
compromising the quality of data
required for bycatch estimation, the
McAllister report raised several issues
related to the analysis conducted in
support of the SBRM Amendment. The
McAllister report claims to have
identified a number of flaws in the
estimation method chosen to be applied
in the SBRM, and that the observer
coverage levels that result from the
application of this estimator could
potentially lead to ‘‘wastage’’ of
government resources because
‘‘unnecessarily high’’ or ‘‘unacceptably
low’’ numbers of observer sea days
could be specified by the SBRM. The
McAllister report claims that the SBRM
Amendment failed to adequately
evaluate the statistical properties of the
six alternative bycatch estimation
methods considered, and raised
concerns that the key assumptions of
the preferred statistical method do not
hold, such that the SBRM Amendment
utilizes a statistical method that is
inferior to others that might have been
selected. The report notes that an
alternative statistical method that was
considered, but not selected, may have
resulted in lower CVs in bycatch
estimates than the other methods. The
McAllister report recommends that
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simulation testing of the candidate
bycatch estimation methods be
conducted to evaluate the potential bias
and precision in the methods prior to
selecting one for implementation.
The McAllister report also raises
concern regarding the degree to which
evidence of bias in the observer data is
acknowledged in the analyses
supporting the SBRM Amendment,
suggesting that there is evidence of bias
in the data where none was reported.
This concern is extended to include the
use of the FVTR as a source of kept
biomass, which may have more bias
than described in the amendment. The
report concludes with the claim that the
SBRM is ‘‘unlikely’’ to provide reliable
discard estimates or prescriptions for
observer coverage, noting that this is
‘‘largely due’’ to the issues previously
raised regarding the ratio bycatch
estimator that was selected.
In spite of the concerns raised, the
McAllister report concedes that ‘‘the
observer data on bycatch appear to be
the best available data on bycatch by
species and fishing fleet type.’’ Dr.
McAllister notes that ‘‘no other data
exist with the extent of coverage of
bycatch species, landed species, and
fishing mode,’’ and that there is a
relatively small proportion of the
various potential combinations of
species and fishing mode for which
observer coverage is too low to permit
estimation of bycatch. The report
acknowledges that there are sufficient
data in the ‘‘vast majority’’ of fishing
mode and species combinations to
enable computation of a bycatch value
and a standard error for the estimate,
and that ‘‘no other type of data collected
comes close to providing the high level
of coverage offered by the existing
observer dataset.’’ The McAllister report
also acknowledges that the high
proportion of the estimates of bycatch
presented in the SBRM with CVs of 30
percent or less indicate that the
‘‘existing observer database has
potential to provide bycatch estimates
with the desired level of precision.’’
In addition to the concerns described
above, the McAllister report also raises
a concern regarding the selection of a 30
percent CV of the discard estimate as an
appropriate performance standard for
the SBRM, noting that in commonly
applied stock assessment models, the
desired CV of the catch estimate would
be 10 percent or less, not 30 percent.
Response: Dr. Murdoch McAllister
makes a number of important comments
on the SBRM Amendment. His thorough
review on behalf of Lenfest Ocean
Program highlights a number of
important issues for discard estimation
and suggests some useful approaches for
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improving the estimators currently
employed. NMFS considered his
comments, but, despite the issues raised
by Dr. McAllister, contends the SBRM is
consistent with all legal and statutory
requirements, and is based upon the
best available science. The SBRM
incorporates not only the sampling
design but also the infrastructure to
collect auxiliary data, the methods of
estimation and the properties of the
estimators, and approaches to improve
the allocation of observer coverage to
the diverse fishing fleets of the
Northeast Region. The SBRM is fully
consistent with the limitations of the
data necessary to support estimation of
discards across a wide range of species
and fisheries.
Improvements can always be made to
statistical models and techniques to
derive bycatch estimates. By reviewing
observer coverage annually and
instituting optimal allocation
procedures, the SBRM is designed to
continuously improve the underlying
data. Ultimately, the utility of any
statistical model depends more on the
quality of the data than the
sophistication of the model.
Nonetheless, the SBRM is designed to
collect data that will support many
different types of statistical estimators.
In order to achieve this goal, the
information in the observed samples
must be sufficient for inference about
the unobserved fraction of the fishery.
The basis for the program rests on the
quality of the discard data collected at
sea by fisheries observers and the ability
to extrapolate estimates of total discards
from the observed fraction of the fleets
to the unobserved fractions. Any
estimator of total discards requires that
the observed rate of discards in a sample
can be expanded to a total. An estimator
based on discards per trip requires an
estimate of total trips; an estimator
based on discards per day absent
requires an estimate of total days absent.
Estimators that compute discard rates as
a function of some set of environmental
conditions or vessel attributes must
have the ability to apply those same
characteristics for the unobserved set.
The remarks of Dr. McAllister appear
to indicate some confusion regarding
the estimators that are applied for the
purpose of initializing the SBRM and
those which will be used in stock
assessments. NMFS acknowledges that
these estimators do not necessarily have
to be the same. In fact, one would
expect that improved discard estimates
can be derived after the data are
collected because more information
about the fishing trip, and the nature of
the discards, is available. Possible
refinements to the data and the resulting
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discard estimates include various poststratification approaches, incorporation
of other auxiliary variables, and
intensive investigation of regulatory
effects (e.g., size limits, trip limits,
overall quotas, closed area effects,
permit restrictions etc.). The ability to
implement these changes is governed
ultimately by the quality of the
statistical sampling design. On that
point, the SBRM is on firm ground:
while the McAllister report provides a
number of instances where further
research efforts can be directed, it does
not alter our conclusion that the SBRM
is a scientifically-sound process for
implementing a continuously improving
process of bycatch estimation.
The SBRM addresses discarding
issues for the entire range of fishing
activities in the Northeast. This synoptic
approach requires careful attention to
the limitations and availability of data
to estimate discards and provides a
representative methodology to apply
consistently across all Northeast Region
fisheries. The inclusion of all species
and all fisheries precluded a detailed
case-by-case treatment of the best
estimators in favor of a standardized
approach to provide reasonable results
across the full range of Northeast Region
fisheries. The SBRM incorporates
objective approaches to reduce the
estimation problem to a subset of cells
that are biologically important.
Dr. McAllister did not comment on
the procedures for collecting data on
trips or the observer training program.
As this was not in his terms of
reference, it is assumed that neither the
Lenfest Ocean Program nor Dr.
McAllister had any serious concerns
about observer training or quality
assurance procedures. The ability to
extrapolate from the observed fishing
trips to the unobserved fraction rests in
part on the overall sampling design. On
this topic, Dr. McAllister states ‘‘In my
view the sampling program proposed for
obtaining bycatch estimates has a few
issues regarding accuracy but largely
appears to be the best available
sampling program for bycatch
estimation.’’
It is noted that, in spite of the
concerns raised, the McAllister report
concedes that ‘‘the observer data on
bycatch appear to be the best available
data on bycatch by species and fishing
fleet type.’’ The author notes that ‘‘no
other data exist with the extent of
coverage of bycatch species, landed
species, and fishing mode,’’ and that
there is a relatively small proportion of
the various potential combinations of
species and fishing mode for which
observer coverage is too low to permit
estimation of bycatch. His report
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acknowledges that there are sufficient
data in the ‘‘vast majority’’ of fishing
mode and species combinations to
enable computation of a bycatch value
and a standard error for the estimate,
and that ‘‘no other type of data collected
comes close to providing the high level
of coverage offered by the existing
observer dataset.’’ The McAllister report
also acknowledges that the high
proportion of the estimates of bycatch
presented in the SBRM with CVs of 30
percent or less indicate that the
‘‘existing observer database has
potential to provide bycatch estimates
with the desired level of precision.’’
Dr. McAllister criticizes the selection
of the ratio estimator as the appropriate
model for estimation. NMFS
acknowledges that the ratio estimator is
not uniformly supported across all 2,700
cells (45 fleets and 60 species groups).
In some instances, the trip-based
estimator (average discards per trip
multiplied by total trips) may in fact
have greater precision. In effect, all of
the discard estimation methods
considered in the SBRM are stratified
ratio estimators. The simple expansion
method preferred by Dr. McAllister uses
total trips as a measure of effort.
Implicitly, this means that the
stratification variables used in the
SBRM are sufficient to define strata with
a low degree of within-stratum
variability and high degree of between
stratum variability. The incorporation of
‘‘days absent’’ as a measure of fishing
effort recognizes that residual variation
in trip length may be important for
characterizing bycatch; however, the
measure of days absent does not account
for variations in transit time to fishing
grounds or search activities (i.e., there
could be significant differences in actual
fishing time true effort if transit time is
accounted for). The use of total landings
addresses this weakness and provides at
least one performance-based measure of
fishing effort, wherein variation in
fishing power can be addressed.
Because catch is the product of effort
and abundance, total landings per trip
can be viewed conceptually as a
surrogate for effective fishing effort, if
average abundance within a year does
not change too greatly.
The SBRM proposes the use of a
stratified ratio estimator as a general
measure of the total bycatch by species.
The estimator incorporates two
complementary components to improve
the precision of the estimates.
Stratification by ‘‘fleets’’ reduces the
variability within non-overlapping sets.
For some species, it would be possible
to develop more refined stratifications,
particularly after the sample has been
collected. Some fleets are strongly
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associated with a particular species,
such as the scallop dredge fleet and the
hydraulic dredge fleet for clams.
However, for most fleets, the target
species is not identifiable in advance.
Some vessels will change net types
during a cruise to shift among species
groups (e.g., gadoids vs. flatfish).
Contrary to the comments of Dr.
McAllister, the estimators used in the
SBRM are consistent with the many
peer-reviewed published studies of
discard estimation. For example, Pikitch
et al. (1998)1 estimated total bycatch for
Pacific halibut as the product of a
bycatch ratio of discard per hour fished
(stratified by fleet, season, and depth)
and total hours fished. Total hours
fished were assumed to have negligible
error because, in the words of the
authors, ‘‘the states of Oregon,
Washington, and California collect
logbooks for the majority of fishing trips
(70–90 percent in Oregon, nearly 100
percent in Washington, and about 80
percent in California).’’ In their paper,
the authors concluded that logbook
records, which McAllister claims are
‘‘notoriously inaccurate,’’ were
sufficient to estimate hours fished even
when they are known to be incomplete.
Stratoudakis et al. (1999)2 recognized
the bias in small sample ratio estimators
and recommended an alternative
method based on collapsed
stratification. The authors examined a
wide range of ratio estimators, similar to
the procedures used in the SBRM. They
recommended the use of a ‘‘partially
collapsed estimator’’ that used total
gadoid landings or total demersal
species landings as the auxiliary
variable in the ratio estimator. They
recommended pooling across strata to
estimate the discard ratio. In the SBRM,
the discard ratio for the ‘‘combined’’
estimator was in fact a ‘‘partially
collapsed estimator’’ over quarters.
Their comparisons of ratio estimators
with the stratified sample mean
estimator suggested improved
performance for most but not all
species. They concluded the partially
collapsed ratio estimator, with gadoid or
total landings as the auxiliary variable,
offers a sensible method for estimating
total species discards within Scottish
waters. Another advantage cited by
these investigators was the decreased
1 Pikitch, E.K., J.R. Wallace, E.A. Babcock, D.L.
Erickson, M. Saelens, and G. Oddsson. 1998. Pacific
halibut bycatch in the Washington, Oregon, and
California groundfish and shrimp trawl fisheries.
North American Journal of Fisheries Management,
18:569-586.
2 Stratoudakis, Y., R.J. Fryer, R.M. Cook, and G.J.
Pierce. 1999. Fish discarded from Scottish demersal
vessels: Estimators of total discards and annual
estimates for targeted gadoids. ICES Journal of
Marine Science, 56:592-605.
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reliance on ad hoc decisions that arise
when single species discard/kept ratios
are employed.
In a comprehensive evaluation of
discarding in the multispecies and
multi-country fisheries of the Northwest
Atlantic, Watson et al. (2000)3 also
estimated total discards by species using
the ratio of discard to total kept.
Previous studies of discarding have also
relied extensively on discard to kept
ratios, and have typically required
pooling of information across fisheries.
Clarke et al. (2002)4 used a discard to
kept ratio to estimate discards of a
squalid shark off the northern coast of
Ireland. They noted that this ratio
‘‘enabled the estimation of the total
weight discarded by raising the overall
discard rate to the reported landings of
the target species.’’ Harrington et al.
(2005)5 and Zeller and Pauly (2005)6
also reported a number of discard
estimates based on discard to kept
ratios.
Allain et al. (2003)7 considered two
methods for estimating the total weights
of fish discarded by the French
grenadier fleet. Extrapolations of total
landings using effort based ratios, as
suggested by McAllister, resulted in
differences between observed and
predicted between -67 and +52 percent
per quarter. They noted that real effort
is difficult to estimate owing to different
fractions of time actually spent on
fishing grounds. Instead, they favored a
target species (grenadier) approach as
the denominator of a discard to kept
ratio because ‘‘it was the target species
of the fishery, it was the only species
both landed and discarded, and it was
the most common species in the catches
of deepwater commercial trawlers.’’
Borges et al. (2005)8 also analyzed
discards at the trip level and considered
four ratio estimators. The authors
3 Watson, R., S. Guennete, P. Fanning, and T.J.
Pitcher. 2000. The basis for change: Part 1,
Reconstructing fisheries catch and effort data. P. 2339 in D. Pauly and T.D Pitcher (eds) Methods for
Assessing the Impacts of Fisheries on Marine
Ecosystems in the North Atlantic. Fisheries Centre
Res. Rep. 8(2), 195 pp.
4 Clarke, M.W., P.L. Connolly, and J.J. Braken.
2005. Catch, discarding, age estimation, growth, and
maturity of the squalid shark, Deania calceus, west
and north of Ireland. Fisheries Research, 55:25-35.
5 Harrington, J.M., R.A. Myers, and A.A.
Rosenberg. 2005. Wasted fishery resources:
Discarded bycatch in the USA. Fish and Fisheries,
6:350-361.
6 Zeller, D. And D. Pauly. 2005. Good new, bad
news: Global fisheries discards are declining, but so
are total catches. Fish and Fisheries, 6:156-150.
7 Allain, V., A. Biseau, and B. Kergoat. 2003.
Preliminary estimates of French deepwater fishery
discards in the Northeast Atlantic Ocean. Fisheries
Research, 60:185-192.
8 Borges L., E. Rogan, and R. Officer. 2005.
Discarding by the demersal fishery in the waters
around Ireland. Fisheries Research, 76:1-13.
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concluded that expansions based on
total trips or total landings were most
appropriate. Their studies suggested
that no single approach may be
appropriate for all fishery strata and that
the performance of the discard to total
kept estimator was sometimes inferior to
a simple discard per trip estimator.
The Food and Agricultural
Organization of the United Nations has
sponsored two of the most
comprehensive estimates of worldwide
discards. The first, by Alverson et al.
(1994),9 estimated total discards by
using ratios of discards to kept of the
same species. The second major paper,
by Kelleher (2005)10, updated the
Alverson et al. review using total
landings in the fleet as the primary
raising factor. The SBRM uses an
approach similar to Kelleher. The focus
is on fisheries rather than target species.
Kelleher argues that the relationship
between landings and discard of a
species is influenced by many different
factors and does not constitute an a
priori basis for estimation of total
discards.
Many attempts in the literature to
model bycatch have been based on
regression trees and Generalized
Additive Models that partition the data
into multiple categories (see
Stratoudakis et al. 199911, Allen et al.
200212, Borges et al. 200513). These
partitions have been based on post hoc
analyses of single species and have been
valuable approaches for improving the
utility of discard estimates. However, it
is not clear how such approaches could
be easily applied in the context of
multivariate responses. The partitioning
of fleets into sectors based on properties
observable before the trip is taken is a
major attribute of the current NEFOP
sampling program (e.g., Cotter et al.
200214, Allen et al. 2002). The ability to
9 Alverson, D.L., M.H. Freeberg, S.A. Murawski,
and J.G. Pope. 1994. A global assessment of
fisheries bycatch and discards. FAO Fisheries
Technical Paper No. 339, 235 pp.
10 Kelleher, K. 2005. Discards in the world’s
marine fisheries: An update. FAO Fisheries
Technical Paper No. 470, 134 pp.
11 Stratoudakis, Y., R.J. Fryer, R.M. Cook, and G.J.
Pierce. 1999. Fish discarded from Scottish demersal
vessels: Estimators of total discards and annual
estimates for targeted gadoids. ICES Journal of
Marine Science, 56:592-605.
12 Allen, M., D. Kilpatrick, M. Armstrong, R.
Briggs, G. Course, and N. Perez. 2002. Multistage
cluster sampling design and optimal sample sizes
for estimation of fish discards from commercial
trawlers. Fisheries Research, 55:11-24.
13 Borges, L., A.F. Zuur, E. Rogan, and R. Officer.
2005. Choosing the best sampling unit and auxiliary
variable for discard estimations. Fisheries Research,
75:29-39.
14 Cotter, A.J.R., G. Course, S.T. Buckland, and C.
Garrod. 2002. A PPS sample survey of English
fishing vessels to estimate discarding and retention
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post-stratify the trips into improved
strata after the trip is taken is a
responsibility of the individual
assessment analyst. The SBRM allows
for this process by ensuring that
whatever assessment methodology is
used, one must consider the total scope
of potential discards across all fleets.
NMFS acknowledges that all
measures of accuracy based on
observations are incomplete, since the
‘‘truth’’ (or its approximation) is
unknown. However, the multiple lines
of evidence used in the SBRM suggest
that potential biases in the NEFOP
observer data do not negate the utility
of all estimates. Several of the data
validation issues highlighted by Dr.
McAllister were examined as part of a
recent Groundfish Assessment Review
Meeting (GARM) held in the fall of
2007. This particular meeting of the
GARM dealt with the catch, survey, and
environmental data that will be used to
assess 19 Northeast groundfish stocks in
2008. The review panel, including its
chair, included eight independent,
external scientists with relevant
experience.
In addition to the methods described
in the SBRM, another validation
approach was presented at the GARM
that included a comparison of total
landings by species estimated from the
observed fraction of the fleet with the
actual landings enumerated in the VTR
data. In other words, an estimate of the
average landings of a single species per
total landings in the observer data was
multiplied by the total landings of all
species in each fleet. If the observer data
are a representative sample, the
confidence interval for estimated total
landings should encompass the true
value. Liggens et al. (1997)15 used a
similar approach for estimating observer
bias by comparing average catch rates
and length frequencies between
observed and unobserved vessels. The
results of this exercise supported the
conclusions presented in the SBRM
Amendment, and confirm that the
method and underlying data provide
sound estimates of discards. For many
species and species groups, the
estimated landings based on NEFOP
data compared favorably to the VTR
landings, with the 95 percent
confidence interval of the estimated
landings encompassing the VTR
landings.
of North Sea cod, haddock, and whiting. Fisheries
Research, 55:25-35.
15 Liggens, G.W., M.J. Bradley, and S.J. Kennelly.
1997. Detection of bias in observer-based estimates
of retained and discarded catches from a multispecies trawl fishery. Fisheries Research, 32:133147.
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The GARM considered this evidence
and concluded that the combined ratio
method was validated by comparing
estimated landings using expanded kept
portion of the catch in the observer data
to the actual report landing. The
estimated landings appear to be in line
with the reported total landings. Using
kept weight of all species in the
denominator of the combined ratio
ensures that all the catch data are used
in estimating discards. The GARM
review panel also concluded that the
SBRM documents a number of
estimators of discarding and validation
of the combined ratio method was
provided using the 2005 observer data
set by a follow-up analysis. VTR data
were used as a surrogate for Dealer data
to expand the NEFOP discard ratios to
total discards. In most cases (95
percent), there was good
correspondence between VTR and
Dealer landings, adding confidence to
the use of these data, although there
were patterns in the data for some
species (e.g., surfclam/quahog, hakes)
that require further exploration. The
GARM concluded that, overall, the
technique was synoptic, reasonably well
validated, and exhibited little evidence
of bias.
Contrary to Dr. McAllister’s
comments, simulation tests of
alternative estimators have been
conducted for several species. These
results were reviewed as part of the
GARM described above. NMFS has also
conducted studies to estimate total
landings from the observed sample data
and have found good agreement for the
methods used in the SBRM. Scientists at
the Northeast Fisheries Science Center
conducted a simulation study of the
behavior of six different estimators of
total discards, including the combined
ratio (discard to kept) and the sample
mean estimator (discard to trip) as
described in the SBRM Amendment.
Results supported the use of the discard
to total kept ratio and the simple
expansion method. The independent
GARM reviewers considered this
additional analysis and concluded that
the analysis provided a comprehensive
simulation study to test the overall
performance of a number of discard
estimation techniques with respect to
bias and precision. Two methods were
clearly superior to the other four
techniques: The SBRM’s combined ratio
estimator (ratio of sums) and the direct
estimator, based on mean discard per
trip scaled up to all trips in the
simulation datasets. The latter had been
advocated by McAllister for the
estimation of discards, and would be the
preferred approach if there is no
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correlation between the numerator and
denominator of the estimate (i.e., there
is no correlation between discard weight
and kept weight). However, the GARM
reviewers concluded that McAllister’s
preferred method only provides
unbiased estimates of total discards if
the total number of trips is known,
which is often not the case in the New
England fisheries. Total landings
estimates are considered more reliable
than those of the total number of trips,
and so the GARM reviewers concluded
that the SBRM’s combined ratio
estimator of mean discard based on
observed trips has the advantage that it
can be combined with known landings
data to estimate total discards. They
considered this to be a pragmatic
solution to data deficiencies, and noted
that the SBRM appears to provide
estimates with similar precision as the
direct estimator. The bias in the
combined ratio estimator depends on
the sample size (number of observed
trips) and was negligible for the data
being assessed in the simulation study.
Regarding the assertion that a CV of
30 percent is an insufficient precision
standard for the SBRM, the commenter
identifies, as a suggested alternative, a
CV of 10 percent for catch estimates
used in stock assessments. However,
NMFS points out that estimates of
bycatch, which are the focus of this
action, are but one aspect of overall
catch, which includes all commercial
and recreational landings as well as
discards. As illustrated in Appendix C
to the SBRM Amendment, for most
species, discards represent a very small
proportion of total catch. Therefore, the
CV of the landings estimates contributes
much more significantly to the CV of the
overall catch than does the CV of the
discard estimate. Also, as explained
earlier, the data generated through the
SBRM are utilized in different ways in
individual stock assessments, and that
post-stratification techniques available
at the individual stock assessment level
provide an opportunity to refine
estimates as Dr. McAllister suggests.
While NMFS agrees that higher
precision is always a laudable goal, it
notes that the Councils’ SSC reviewers,
as well as another independent scientist
commenting on the SBRM Amendment
(see comment 8), all concluded that the
proposed standard of a CV of 30 percent
is appropriate for its stated purpose.
In sum, NMFS has carefully
considered the comments and
suggestions made by Dr. McAllister, in
some cases conducting additional
analyses which have been subjected to
an additional level of independent
external peer review through the GARM,
and found that none of the comments
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undermine NMFS’s findings regarding
the adequacy of the Northeast Region
SBRM.
Comment 11: One member of the
public expressed concern over whether
the agency may be unduly swayed in
the actions it takes due to political
interference. The commenter suggested
that all fishing quotas be cut by 50
percent, but no evidence or analysis was
provided to support such a reduction.
Response: This comment letter did
not address the specific provisions of
the SBRM Amendment or its proposed
rule, and the comments have no bearing
on the agency’s decision relative to this
action.
Classification
The Administrator, Northeast Region,
NMFS, determined that the Northeast
Region SBRM Omnibus Amendment is
necessary for the conservation and
management of Northeast Region
fisheries and that it is consistent with
the Magnuson-Stevens Act and other
applicable laws.
This final rule has been determined to
be not significant for purposes of
Executive Order 12866.
The Chief Counsel for Regulation of
the Department of Commerce certified
to the Chief Counsel for Advocacy of the
Small Business Administration during
the proposed rule stage that this action
would not have a significant economic
impact on a substantial number of small
entities. The factual basis for the
certification was published in the
proposed rule and is not repeated here.
No comments were received regarding
this certification. As a result, a
regulatory flexibility analysis was not
required and none was prepared.
Dated: January 22, 2008
Samuel D. Rauch III
Deputy Assistant Administrator For
Regulatory Programs, National Marine
Fisheries Service
For the reasons set out in the
preamble, 50 CFR part 648 is amended
as follows:
I
PART 648—FISHERIES OF THE
NORTHEASTERN UNITED STATES
1. The authority citation for part 648
continues to read as follows:
Authority: 16 U.S.C. 1801 et seq.
2. In § 648.11, paragraphs (h) and (i)
are revised to read as follows:
I
§ 648.11 At-sea sea sampler/observer
coverage.
*
*
*
*
*
(h) Observer service provider approval
and responsibilities—(1) General. An
entity seeking to provide observer
services must apply for and obtain
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approval from NMFS following
submission of a complete application to
The Observer Program Branch Chief, 25
Bernard St Jean Drive, East Falmouth,
MA 02536. A list of approved observer
service providers shall be distributed to
vessel owners and shall be posted on
the NMFS/NEFOP website at https://
www.nefsc.noaa.gov/femad/fsb/.
(2) Existing observer service providers.
Observer service providers that
currently deploy certified observers in
the Northeast must submit an
application containing the information
specified in paragraph (h)(3) of this
section, excluding any information
specified in paragraph (h)(3) of this
section that has already been submitted
to NMFS.
(3) Contents of application. An
application to become an approved
observer service provider shall contain
the following:
(i) Identification of the management,
organizational structure, and ownership
structure of the applicant’s business,
including identification by name and
general function of all controlling
management interests in the company,
including but not limited to owners,
board members, officers, authorized
agents, and staff. If the applicant is a
corporation, the articles of incorporation
must be provided. If the applicant is a
partnership, the partnership agreement
must be provided.
(ii) The permanent mailing address,
phone and fax numbers where the
owner(s) can be contacted for official
correspondence, and the current
physical location, business mailing
address, business telephone and fax
numbers, and business e-mail address
for each office.
(iii) A statement, signed under
penalty of perjury, from each owner or
owners, board members, and officers, if
a corporation, that they are free from a
conflict of interest as described under
paragraph (h)(6) of this section.
(iv) A statement, signed under penalty
of perjury, from each owner or owners,
board members, and officers, if a
corporation, describing any criminal
convictions, Federal contracts they have
had, and the performance rating they
received on the contract, and previous
decertification action while working as
an observer or observer service provider.
(v) A description of any prior
experience the applicant may have in
placing individuals in remote field and/
or marine work environments. This
includes, but is not limited to,
recruiting, hiring, deployment, and
personnel administration.
(vi) A description of the applicant’s
ability to carry out the responsibilities
and duties of a fishery observer services
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provider as set out under paragraph
(h)(2) of this section, and the
arrangements to be used.
(vii) Evidence of holding adequate
insurance to cover injury, liability, and
accidental death for observers during
their period of employment (including
during training). Workers’
Compensation and Maritime Employer’s
Liability insurance must be provided to
cover the observer, vessel owner, and
observer provider. The minimum
coverage required is $5 million.
Observer service providers shall provide
copies of the insurance policies to
observers to display to the vessel owner,
operator, or vessel manager, when
requested.
(viii) Proof that its observers, either
contracted or employed by the service
provider, are compensated with salaries
that meet or exceed the U.S. Department
of Labor (DOL) guidelines for observers.
Observers shall be compensated as a
Fair Labor Standards Act (FLSA) nonexempt employees. Observer providers
shall provide any other benefits and
personnel services in accordance with
the terms of each observer’s contract or
employment status.
(ix) The names of its fully equipped,
NMFS/NEFOP certified, observers on
staff or a list of its training candidates
(with resumes) and a request for an
appropriate NMFS/NEFOP Observer
Training class. The NEFOP training has
a minimum class size of eight
individuals, which may be split among
multiple vendors requesting training.
Requests for training classes with less
than eight individuals will be delayed
until further requests make up the full
training class size. Requests for training
classes must be made 30 days in
advance of the requested date and must
have a complete roster of trainees at that
time.
(x) An Emergency Action Plan (EAP)
describing its response to an ‘‘at sea’’
emergency with an observer, including,
but not limited to, personal injury,
death, harassment, or intimidation.
(4) Application evaluation. (i) NMFS
shall review and evaluate each
application submitted under paragraphs
(h)(2) and (h)(3) of this section. Issuance
of approval as an observer provider
shall be based on completeness of the
application, and a determination of the
applicant’s ability to perform the duties
and responsibilities of a fishery observer
service provider, as demonstrated in the
application information. A decision to
approve or deny an application shall be
made by NMFS within 15 business days
of receipt of the application by NMFS.
(ii) If NMFS approves the application,
the observer service provider’s name
will be added to the list of approved
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observer service providers found on the
NMFS/NEFOP website specified in
paragraph (h)(1) of this section, and in
any outreach information to the
industry. Approved observer service
providers shall be notified in writing
and provided with any information
pertinent to its participation in the
fishery observer program.
(iii) An application shall be denied if
NMFS determines that the information
provided in the application is not
complete or the evaluation criteria are
not met. NMFS shall notify the
applicant in writing of any deficiencies
in the application or information
submitted in support of the application.
An applicant who receives a denial of
his or her application may present
additional information to rectify the
deficiencies specified in the written
denial, provided such information is
submitted to NMFS within 30 days of
the applicant’s receipt of the denial
notification from NMFS. In the absence
of additional information, and after 30
days from an applicant’s receipt of a
denial, an observer provider is required
to resubmit an application containing
all of the information required under the
application process specified in
paragraph (h)(3) of this section to be reconsidered for being added to the list of
approved observer service providers.
(5) Responsibilities of observer service
providers. (i) An observer service
provider must provide observers
certified by NMFS/NEFOP pursuant to
paragraph (i) of this section for
deployment in a fishery when contacted
and contracted by the owner, operator,
or vessel manager of a vessel fishing,
unless the observer service provider
refuses to deploy an observer on a
requesting vessel for any of the reasons
specified at paragraph (h)(5)(viii) of this
section. An approved observer service
provider must maintain a minimum of
eight appropriately trained NEFOP
certified observers in order to remain
approved; should a service provider
cadre drop below eight, the provider
must submit the appropriate number of
candidates for the next available
training class. Failure to do so shall be
cause for suspension of their approved
status until rectified.
(ii) An observer service provider must
provide to each of its observers:
(A) All necessary transportation,
including arrangements and logistics, of
observers to the initial location of
deployment, to all subsequent vessel
assignments, and to any debriefing
locations, if necessary;
(B) Lodging, per diem, and any other
services necessary for observers
assigned to a fishing vessel or to attend
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4751
an appropriate NMFS/NEFOP Observer
Training class;
(C) The required observer equipment,
in accordance with equipment
requirements listed on the NMFS/
NEFOP website specified in paragraph
(h)(1) of this section, prior to any
deployment and/or prior to NMFS
observer certification training; and
(D) Individually assigned
communication equipment, in working
order, such as a cell phone or pager, for
all necessary communication. An
observer service provider may
alternatively compensate observers for
the use of the observer’s personal cell
phone or pager for communications
made in support of, or necessary for, the
observer’s duties.
(iii) Observer deployment logistics.
Each approved observer service
provider must assign an available
certified observer to a vessel upon
request. Each approved observer service
provider must provide for access by
industry 24 hours per day, 7 days per
week, to enable an owner, operator, or
manager of a vessel to secure observer
coverage when requested. The
telephone system must be monitored a
minimum of four times daily to ensure
rapid response to industry requests.
Observer service providers approved
under paragraph (h) of this section are
required to report observer deployments
to NMFS daily for the purpose of
determining whether the predetermined
coverage levels are being achieved in
the appropriate fishery.
(iv) Observer deployment limitations.
Unless alternative arrangements are
approved by NMFS, an observer
provider must not deploy any observer
on the same vessel for two or more
consecutive deployments, and not more
than twice in any given month. A
certified observer’s first deployment and
the resulting data shall be immediately
edited, and approved, by NMFS prior to
any further deployments of that
observer.
(v) Communications with observers.
An observer service provider must have
an employee responsible for observer
activities on call 24 hours a day to
handle emergencies involving observers
or problems concerning observer
logistics, whenever observers are at sea,
stationed shoreside, in transit, or in port
awaiting vessel assignment.
(vi) Observer training requirements.
The following information must be
submitted to NMFS to request a certified
observer training class at least 30 days
prior to the beginning of the proposed
training class: Date of requested
training; a list of observer candidates,
with a minimum of eight individuals;
observer candidate resumes; and a
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statement signed by the candidate,
under penalty of perjury, that discloses
the candidate’s criminal convictions, if
any. All observer trainees must
complete a basic cardiopulmonary
resuscitation/first aid course prior to the
beginning of a NMFS/NEFOP Observer
Training class. NMFS may reject a
candidate for training if the candidate
does not meet the minimum
qualification requirements as outlined
by NMFS National Minimum Eligibility
Standards for observers as described in
paragraph (i)(1) of this section.
(vii) Reports—(A) Observer
deployment reports. The observer
service provider must report to NMFS
when, where, to whom, and to what
fishery an observer has been deployed,
within 24 hours of their departure. The
observer service provider must ensure
that the observer reports back to NMFS
its Observer Contract (OBSCON) data, as
described in the certified observer
training, within 12 hours of landing.
OBSCON data are to be submitted
electronically or by other means as
specified by NMFS. The observer
service provider shall provide the raw
(unedited) data collected by the
observer to NMFS within 72 hours of
the trip landing.
(B) Safety refusals. The observer
service provider must report to NMFS
any trip that has been refused due to
safety issues, e.g., failure to hold a valid
USCG Commercial Fishing Vessel Safety
Examination Decal or to meet the safety
requirements of the observer’s pre-trip
vessel safety checklist, within 24 hours
of the refusal.
(C) Biological samples. The observer
service provider must ensure that
biological samples, including whole
marine mammals, sea turtles, and sea
birds, are stored/handled properly and
transported to NMFS within 7 days of
landing.
(D) Observer debriefing. The observer
service provider must ensure that the
observer remains available to NMFS,
including NMFS Office for Law
Enforcement, for debriefing for at least
2 weeks following any observed trip. If
requested by NMFS, an observer that is
at sea during the 2-week period must
contact NMFS upon his or her return.
(E) Observer availability report. The
observer service provider must report to
NMFS any occurrence of inability to
respond to an industry request for
observer coverage due to the lack of
available observers on staff by 5 pm,
Eastern Standard Time, of any day on
which the provider is unable to respond
to an industry request for observer
coverage.
(F) Other reports. The observer
provider must report possible observer
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harassment, discrimination, concerns
about vessel safety or marine casualty,
observer illness or injury, and any
information, allegations, or reports
regarding observer conflict of interest or
breach of the standards of behavior must
be submitted to NMFS within 24 hours
of the event or within 24 hours of
learning of the event.
(viii) Refusal to deploy an observer.
(A) An observer service provider may
refuse to deploy an observer on a
requesting fishing vessel if the observer
service provider does not have an
available observer within 72 hours of
receiving a request for an observer from
a vessel.
(B) An observer service provider may
refuse to deploy an observer on a
requesting fishing vessel if the observer
service provider has determined that the
requesting vessel is inadequate or
unsafe pursuant to the reasons
described at§ 600.746.
(C) The observer service provider may
refuse to deploy an observer on a fishing
vessel that is otherwise eligible to carry
an observer for any other reason,
including failure to pay for previous
observer deployments, provided the
observer service provider has received
prior written confirmation from NMFS
authorizing such refusal.
(6) Limitations on conflict of interest.
An observer service provider:
(i) Must not have a direct or indirect
interest in a fishery managed under
Federal regulations, including, but not
limited to, a fishing vessel, fish dealer,
fishery advocacy group, and/or fishery
research;
(ii) Must assign observers without
regard to any preference by
representatives of vessels other than
when an observer will be deployed; and
(iii) Must not solicit or accept,
directly or indirectly, any gratuity, gift,
favor, entertainment, loan, or anything
of monetary value from anyone who
conducts fishing or fishing related
activities that are regulated by NMFS, or
who has interests that may be
substantially affected by the
performance or nonperformance of the
official duties of observer providers.
(7) Removal of observer service
provider from the list of approved
observer service providers. An observer
provider that fails to meet the
requirements, conditions, and
responsibilities specified in paragraphs
(h)(5) and (h)(6) of this section shall be
notified by NMFS, in writing, that it is
subject to removal from the list of
approved observer service providers.
Such notification shall specify the
reasons for the pending removal. An
observer service provider that has
received notification that it is subject to
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removal from the list of approved
observer service providers may submit
information to rebut the reasons for
removal from the list. Such rebuttal
must be submitted within 30 days of
notification received by the observer
service provider that the observer
service provider is subject to removal
and must be accompanied by written
evidence that clearly disproves the
reasons for removal. NMFS shall review
information rebutting the pending
removal and shall notify the observer
service provider within 15 days of
receipt of the rebuttal whether or not the
removal is warranted. If no response to
a pending removal is received by NMFS,
the observer service provider shall be
automatically removed from the list of
approved observer service providers.
The decision to remove the observer
service provider from the list, either
after reviewing a rebuttal, or if no
rebuttal is submitted, shall be the final
decision of NMFS and the Department
of Commerce. Removal from the list of
approved observer service providers
does not necessarily prevent such
observer service provider from obtaining
an approval in the future if a new
application is submitted that
demonstrates that the reasons for
removal are remedied. Certified
observers under contract with an
observer service provider that has been
removed from the list of approved
service providers must complete their
assigned duties for any fishing trips on
which the observers are deployed at the
time the observer service provider is
removed from the list of approved
observer service providers. An observer
service provider removed from the list
of approved observer service providers
is responsible for providing NMFS with
the information required in paragraph
(h)(5)(vii) of this section following
completion of the trip. NMFS may
consider, but is not limited to, the
following in determining if an observer
service provider may remain on the list
of approved observer service providers:
(i) Failure to meet the requirements,
conditions, and responsibilities of
observer service providers specified in
paragraphs (h)(5) and (h)(6) of this
section;
(ii) Evidence of conflict of interest as
defined under paragraph (h)(3) of this
section;
(iii) Evidence of criminal convictions
related to:
(A) Embezzlement, theft, forgery,
bribery, falsification or destruction of
records, making false statements, or
receiving stolen property; or
(B) The commission of any other
crimes of dishonesty, as defined by state
law or Federal law that would seriously
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and directly affect the fitness of an
applicant in providing observer services
under this section;
(iv) Unsatisfactory performance
ratings on any Federal contracts held by
the applicant; and
(v) Evidence of any history of
decertification as either an observer or
observer provider.
(i) Observer certification. (1) To be
certified, employees or sub-contractors
operating as observers for observer
service providers approved under
paragraph (h) of this section must meet
NMFS National Minimum Eligibility
Standards for observers. NMFS National
Minimum Eligibility Standards are
available at the National Observer
Program website: https://
www.st.nmfs.gov/st4/nop/.
(2) Observer training. In order to be
deployed on any fishing vessel, a
candidate observer must have passed an
appropriate NMFS/NEFOP Observer
Training course. If a candidate fails
training, the candidate shall be notified
in writing on or before the last day of
training. The notification will indicate
the reasons the candidate failed the
training. Observer training shall include
an observer training trip, as part of the
observer’s training, aboard a fishing
vessel with a trainer. A certified
observer’s first deployment and the
resulting data shall be immediately
edited, and approved, by NMFS prior to
any further deployments of that
observer.
(3) Observer requirements. All
observers must:
(i) Have a valid NMFS/NEFOP
fisheries observer certification pursuant
to paragraph (i)(1) of this section;
(ii) Be physically and mentally
capable of carrying out the
responsibilities of an observer on board
fishing vessels, pursuant to standards
established by NMFS. Such standards
are available from NMFS/NEFOP
website specified in paragraph (h)(1) of
this section and shall be provided to
each approved observer service
provider;
(iii) Have successfully completed all
NMFS-required training and briefings
for observers before deployment,
pursuant to paragraph (i)(2) of this
section; and
(iv) Hold a current Red Cross (or
equivalence) CPR/first aid certification.
(4) Probation and decertification.
NMFS has the authority to review
observer certifications and issue
observer certification probation and/or
decertification as described in NMFS
policy found on the NMFS/NEFOP
website specified in paragraph (h)(1) of
this section.
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(5) Issuance of decertification. Upon
determination that decertification is
warranted under paragraph (i)(3) of this
section, NMFS shall issue a written
decision to decertify the observer to the
observer and approved observer service
providers via certified mail at the
observer’s most current address
provided to NMFS. The decision shall
identify whether a certification is
revoked and shall identify the specific
reasons for the action taken.
Decertification is effective immediately
as of the date of issuance, unless the
decertification official notes a
compelling reason for maintaining
certification for a specified period and
under specified conditions.
Decertification is the final decision of
NMFS and the Department of Commerce
and may not be appealed.
I 3. Add § 648.18 to subpart A to read
as follows:
§ 648.18 Standardized bycatch reporting
methodology.
NMFS shall comply with the
Standardized Bycatch Reporting
Methodology (SBRM) provisions
established in the following fishery
management plans: Atlantic Bluefish;
Atlantic Herring; Atlantic Salmon;
Deep-Sea Red Crab; Mackerel, Squid,
and Butterfish; Monkfish; Northeast
Multispecies; Northeast Skate Complex;
Sea Scallop; Spiny Dogfish; Summer
Flounder, Scup, and Black Sea Bass;
Surfclam and Ocean Quahog; and
Tilefish.
I 4. In § 648.21, paragraph (c)(13) is
added to read as follows:
§ 648.21 Procedures for determining initial
annual amounts.
(c) * * *
(13) Changes, as appropriate, to the
Northeast Region SBRM, including the
coefficient of variation (CV) based
performance standard, fishery
stratification, and/or reports.
*
*
*
*
*
I 5. In § 648.24, paragraph (a)(1) is
revised to read as follows:
§ 648.24 Framework adjustments to
management measures.
(a) * * *
(1) Adjustment process. The Council
shall develop and analyze appropriate
management actions over the span of at
least two Council meetings. The Council
must provide the public with advance
notice of the availability of the
recommendation(s), appropriate
justification(s) and economic and
biological analyses, and the opportunity
to comment on the proposed
adjustment(s) at the first meeting and
prior to and at the second Council
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4753
meeting. The Council’s
recommendations on adjustments or
additions to management measures
must come from one or more of the
following categories: Minimum fish
size, maximum fish size, gear
restrictions, gear requirements or
prohibitions, permitting restrictions,
recreational possession limit,
recreational seasons, closed areas,
commercial seasons, commercial trip
limits, commercial quota system
including commercial quota allocation
procedure and possible quota set asides
to mitigate bycatch, recreational harvest
limit, annual specification quota setting
process, FMP Monitoring Committee
composition and process, description
and identification of EFH (and fishing
gear management measures that impact
EFH), description and identification of
habitat areas of particular concern,
overfishing definition and related
thresholds and targets, regional gear
restrictions, regional season restrictions
(including option to split seasons),
restrictions on vessel size (LOA and
GRT) or shaft horsepower, changes to
the Northeast Region SBRM (including
the CV-based performance standard, the
means by which discard data are
collected/obtained, fishery stratification,
reports, and/or industry-funded
observers or observer set-aside
programs), any other management
measures currently included in the
FMP, set aside quota for scientific
research, regional management, and
process for inseason adjustment to the
annual specification.
*
*
*
*
*
I 6. In § 648.55, paragraph (e)(32) is
revised and paragraph (e)(33) is added
to read as follows:
§ 648.55 Framework adjustments to
management measures.
*
*
*
*
*
(e) * * *
(32) Changes to the Northeast Region
SBRM, including the CV-based
performance standard, the means by
which discard data are collected/
obtained, fishery stratification, reports,
and/or industry-funded observers or
observer set-aside programs.
(33) Any other management measures
currently included in the FMP.
*
*
*
*
*
I 7. In § 648.77, paragraph (a)(1) is
revised to read as follows:
§ 648.77 Framework adjustments to
management measures.
(a) * * *
(1) Adjustment process. The Council
shall develop and analyze appropriate
management actions over the span of at
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least two Council meetings. The Council
must provide the public with advance
notice of the availability of the
recommendation(s), appropriate
justification(s) and economic and
biological analyses, and the opportunity
to comment on the proposed
adjustment(s) at the first meeting, and
prior to and at the second Council
meeting. The Council’s
recommendations on adjustments or
additions to management measures
must come from one or more of the
following categories: The overfishing
definition (both the threshold and target
levels), description and identification of
EFH (and fishing gear management
measures that impact EFH), habitat
areas of particular concern, set-aside
quota for scientific research, VMS, OY
range, suspension or adjustment of the
surfclam minimum size limit, and
changes to the Northeast Region SBRM
(including the CV-based performance
standard, the means by which discard
data are collected/obtained, fishery
stratification, reports, and/or industryfunded observers or observer set-aside
programs).
*
*
*
*
*
I 8. In § 648.90, paragraphs (a)(2)(i),
(a)(2)(iii), (b)(1)(ii), and (c)(1)(i) are
revised to read as follows:
§ 648.90 NE Multispecies assessment,
framework procedures and specifications,
and flexible area action system.
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*
*
*
*
*
(a) * * *
(2) Biennial review. (i) Beginning in
2005, the NE Multispecies PDT shall
meet on or before September 30 every
other year, unless otherwise specified in
paragraph (a)(3) of this section, under
the conditions specified in that
paragraph, to perform a review of the
fishery, using the most current scientific
information available provided
primarily from the NEFSC. Data
provided by states, ASMFC, the USCG,
and other sources may also be
considered by the PDT. Based on this
review, the PDT will develop target
TACs for the upcoming fishing year(s)
and develop options for Council
consideration, if necessary, on any
changes, adjustments, or additions to
DAS allocations, closed areas, or on
other measures necessary to achieve the
FMP goals and objectives, including
changes to the Northeast Region SBRM.
For the 2005 biennial review, an
updated groundfish assessment, peerreviewed by independent scientists, will
be conducted to facilitate the PDT
review for the biennial adjustment, if
needed, for the 2006 fishing year.
Amendment 13 biomass and fishing
mortality targets may not be modified by
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the 2006 biennial adjustment unless
review of all valid pertinent scientific
work during the 2005 review process
justifies consideration.
*
*
*
*
*
(iii) Based on this review, the PDT
shall recommend target TACs and
develop options necessary to achieve
the FMP goals and objectives, which
may include a preferred option. The
PDT must demonstrate through analyses
and documentation that the options
they develop are expected to meet the
FMP goals and objectives. The PDT may
review the performance of different user
groups or fleet Sectors in developing
options. The range of options developed
by the PDT may include any of the
management measures in the FMP,
including, but not limited to: Target
TACs, which must be based on the
projected fishing mortality levels
required to meet the goals and
objectives outlined in the FMP for the
10 regulated species, Atlantic halibut (if
able to be determined), and ocean pout;
DAS changes; possession limits; gear
restrictions; closed areas; permitting
restrictions; minimum fish sizes;
recreational fishing measures;
description and identification of EFH;
fishing gear management measures to
protect EFH; designation of habitat areas
of particular concern within EFH; and
changes to the Northeast Region SBRM,
including the CV-based performance
standard, the means by which discard
data are collected/obtained, fishery
stratification, reports, and/or industryfunded observers or observer set-aside
programs. In addition, the following
conditions and measures may be
adjusted through future framework
adjustments: Revisions to status
determination criteria, including, but
not limited to, changes in the target
fishing mortality rates, minimum
biomass thresholds, numerical estimates
of parameter values, and the use of a
proxy for biomass; DAS allocations
(such as the category of DAS under the
DAS reserve program, etc.) and DAS
baselines, etc.; modifications to capacity
measures, such as changes to the DAS
transfer or DAS leasing measures;
calculation of area-specific TACs, area
management boundaries, and adoption
of area-specific management measures;
Sector allocation requirements and
specifications, including establishment
of a new Sector; measures to implement
the U.S./Canada Resource Sharing
Understanding, including any specified
TACs (hard or target); changes to
administrative measures; additional
uses for Regular B DAS; future uses for
C DAS; reporting requirements; the
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Management Stewardship Plan; GB Cod
Gillnet Sector allocation; allowable
percent of TAC available to a Sector
through a Sector allocation;
categorization of DAS; DAS leasing
provisions; adjustments for steaming
time; adjustments to the Handgear A
permit; gear requirements to improve
selectivity, reduce bycatch, and/or
reduce impacts of the fishery on EFH;
SAP modifications; and any other
measures currently included in the
FMP.
*
*
*
*
*
(b) * * *
(1) * * *
(ii) The WMC shall recommend
management options necessary to
achieve FMP goals and objectives
pertaining to small-mesh multispecies,
which may include a preferred option.
The WMC must demonstrate through
analyses and documentation that the
options it develops are expected to meet
the FMP goals and objectives. The WMC
may review the performance of different
user groups or fleet Sectors in
developing options. The range of
options developed by the WMC may
include any of the management
measures in the FMP, including, but not
limited to: Annual target TACs, which
must be based on the projected fishing
mortality levels required to meet the
goals and objectives outlined in the
FMP for the small-mesh multispecies;
possession limits; gear restrictions;
closed areas; permitting restrictions;
minimum fish sizes; recreational fishing
measures; description and identification
of EFH; fishing gear management
measures to protect EFH; designation of
habitat areas of particular concern
within EFH; changes to the Northeast
Region SBRM, including the CV-based
performance standard, the means by
which discard data are collected/
obtained, fishery stratification, reports,
and/or industry-funded observers or
observer set-aside programs; and any
other management measures currently
included in the FMP.
*
*
*
*
*
(c) * * *
(1) * * *
(i) After a management action has
been initiated, the Council shall develop
and analyze appropriate management
actions over the span of at least two
Council meetings. The Council shall
provide the public with advance notice
of the availability of both the proposals
and the analyses and opportunity to
comment on them prior to and at the
second Council meeting. The Council’s
recommendation on adjustments or
additions to management measures,
other than to address gear conflicts,
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must come from one or more of the
following categories: DAS changes,
effort monitoring, data reporting,
possession limits, gear restrictions,
closed areas, permitting restrictions,
crew limits, minimum fish sizes,
onboard observers, minimum hook size
and hook style, the use of crucifer in the
hook-gear fishery, fleet Sector shares,
recreational fishing measures, area
closures and other appropriate measures
to mitigate marine mammal
entanglements and interactions,
description and identification of EFH,
fishing gear management measures to
protect EFH, designation of habitat areas
of particular concern within EFH,
changes to the Northeast Region SBRM,
and any other management measures
currently included in the FMP. In
addition, the Council’s recommendation
on adjustments or additions to
management measures pertaining to
small-mesh NE multispecies, other than
to address gear conflicts, must come
from one or more of the following
categories: Quotas and appropriate
seasonal adjustments for vessels fishing
in experimental or exempted fisheries
that use small mesh in combination
with a separator trawl/grate (if
applicable), modifications to separator
grate (if applicable) and mesh
configurations for fishing for smallmesh NE multispecies, adjustments to
whiting stock boundaries for
management purposes, adjustments for
fisheries exempted from minimum mesh
requirements to fish for small-mesh NE
multispecies (if applicable), season
adjustments, declarations, participation
requirements for the Cultivator Shoal
Whiting Fishery Exemption Area, and
changes to the Northeast Region SBRM
(including the CV-based performance
standard, the means by which discard
data are collected/obtained, fishery
stratification, reports, and/or industryfunded observers or observer set-aside
programs).
*
*
*
*
*
I 9. In § 648.96, the section heading,
paragraphs (a), (b)(5), and (c)(1)(i) are
revised to read as follows:
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§ 648.96 Monkfish annual adjustment
process and framework specifications.
(a) General. The Monkfish Monitoring
Committee (MFMC) shall meet on or
before November 15 of each year to
develop target TACs for the upcoming
fishing year in accordance with
paragraph (b)(1) of this section, and
options for NEFMC and MAFMC
consideration on any changes,
adjustment, or additions to DAS
allocations, trip limits, size limits, the
Northeast Region SBRM (including the
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CV-based performance standard, fishery
stratification, and/or reports), or other
measures necessary to achieve the
Monkfish FMP’s goals and objectives.
The MFMC shall review available data
pertaining to discards and landings,
DAS, and other measures of fishing
effort; stock status and fishing mortality
rates; enforcement of and compliance
with management measures; and any
other relevant information.
(b) * * *
(5) Annual review process. The
Monkfish Monitoring Committee
(MFMC) shall meet on or before
November 15 of each year to develop
options for the upcoming fishing year,
as needed, and options for NEFMC and
MAFMC consideration on any changes,
adjustment, or additions to DAS
allocations, trip limits, size limits, the
Northeast Region SBRM (including the
CV-based performance standard, fishery
stratification, and/or reports), or other
measures necessary to achieve the
Monkfish FMP’s goals and objectives.
The MFMC shall review available data
pertaining to discards and landings,
DAS, and other measures of fishing
effort; stock status and fishing mortality
rates; enforcement of and compliance
with management measures; and any
other relevant information.
*
*
*
*
*
(c) * * *
(1) * * *
(i) Based on their annual review, the
MFMC may develop and recommend, in
addition to the target TACs and
management measures established
under paragraph (b) of this section,
other options necessary to achieve the
Monkfish FMP’s goals and objectives,
which may include a preferred option.
The MFMC must demonstrate through
analysis and documentation that the
options it develops are expected to meet
the Monkfish FMP goals and objectives.
The MFMC may review the performance
of different user groups or fleet sectors
in developing options. The range of
options developed by the MFMC may
include any of the management
measures in the Monkfish FMP,
including, but not limited to: Closed
seasons or closed areas; minimum size
limits; mesh size limits; net limits; liverto-monkfish landings ratios; annual
monkfish DAS allocations and
monitoring; trip or possession limits;
blocks of time out of the fishery; gear
restrictions; transferability of permits
and permit rights or administration of
vessel upgrades, vessel replacement, or
permit assignment; measures to
minimize the impact of the monkfish
fishery on protected species; gear
requirements or restrictions that
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4755
minimize bycatch or bycatch mortality;
transferable DAS programs; changes to
the Northeast Region SBRM, including
the CV-based performance standard, the
means by which discard data are
collected/obtained, fishery stratification,
reports, and/or industry-funded
observers or observer set-aside
programs; and other frameworkable
measures included in §§ 648.55 and
648.90.
*
*
*
*
*
I 10. In § 648.100, paragraph (a) is
revised and paragraph (b)(12) is added
to read as follows:
§ 648.100 Catch quotas and other
restrictions.
(a) Review. The Summer Flounder
Monitoring Committee shall review
each year the following data, subject to
availability, unless a TAL has already
been established for the upcoming
calendar year as part of a multiple-year
specification process, provided that new
information does not require a
modification to the multiple-year
quotas, to determine the annual
allowable levels of fishing and other
restrictions necessary to achieve, with at
least a 50–percent probability of
success, a fishing mortality rate (F) that
produces the maximum yield per recruit
(Fmax): Commercial, recreational, and
research catch data; current estimates of
fishing mortality; stock status; recent
estimates of recruitment; virtual
population analysis results; levels of
noncompliance by fishermen or
individual states; impact of size/mesh
regulations; discards; sea sampling and
winter trawl survey data or, if sea
sampling data are unavailable, length
frequency information from the winter
trawl survey and mesh selectivity
analyses; impact of gear other than otter
trawls on the mortality of summer
flounder; and any other relevant
information.
(b) * * *
(12) Changes, as appropriate, to the
Northeast Region SBRM, including the
CV-based performance standard, fishery
stratification, and/or reports.
*
*
*
*
*
I 11. In § 648.108, paragraph (a)(1) is
revised to read as follows:
§ 648.108 Framework adjustments to
management measures.
(a) * * *
(1) Adjustment process. The Council
shall develop and analyze appropriate
management actions over the span of at
least two Council meetings. The Council
must provide the public with advance
notice of the availability of the
recommendation(s), appropriate
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justification(s) and economic and
biological analyses, and the opportunity
to comment on the proposed
adjustment(s) at the first meeting and
prior to and at the second Council
meeting. The Council’s
recommendations on adjustments or
additions to management measures
must come from one or more of the
following categories: Minimum fish
size, maximum fish size, gear
restrictions, gear requirements or
prohibitions, permitting restrictions,
recreational possession limit,
recreational seasons, closed areas,
commercial seasons, commercial trip
limits, commercial quota system
including commercial quota allocation
procedure and possible quota set asides
to mitigate bycatch, recreational harvest
limit, annual specification quota setting
process, FMP Monitoring Committee
composition and process, description
and identification of essential fish
habitat (and fishing gear management
measures that impact EFH), description
and identification of habitat areas of
particular concern, overfishing
definition and related thresholds and
targets, regional gear restrictions,
regional season restrictions (including
option to split seasons), restrictions on
vessel size (LOA and GRT) or shaft
horsepower, operator permits, changes
to the Northeast Region SBRM
(including the CV-based performance
standard, the means by which discard
data are collected/obtained, fishery
stratification, reports, and/or industryfunded observers or observer set-aside
programs), any other commercial or
recreational management measures, any
other management measures currently
included in the FMP, and set aside
quota for scientific research.
*
*
*
*
*
I 12. In § 648.120, paragraph (a) is
revised and paragraph (b)(13) is added
to read as follows:
sroberts on PROD1PC70 with RULES
§ 648.120 Catch quotas and other
restrictions.
(a) Review. The Scup Monitoring
Committee shall review each year the
following data, subject to availability,
unless a TAL already has been
established for the upcoming calendar
year as part of a multiple-year
specification process, provided that new
information does not require a
modification to the multiple-year
quotas: Commercial, recreational, and
research data; current estimates of
fishing mortality; stock status; recent
estimates of recruitment; virtual
population analysis results; levels of
noncompliance by fishermen or
individual states; impact of size/mesh
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regulations; impact of gear on the
mortality of scup; discards; and any
other relevant information. This review
will be conducted to determine the
allowable levels of fishing and other
restrictions necessary to achieve the F
that produces the maximum yield per
recruit (Fmax).
(b) * * *
(13) Changes, as appropriate, to the
Northeast Region SBRM, including the
CV-based performance standard, fishery
stratification, and/or reports.
*
*
*
*
*
I 13. In § 648.140, paragraph (a) is
revised and paragraph (b)(12) is added
to read as follows:
§ 648.140 Catch quotas and other
restrictions.
(a) Review. The Black Sea Bass
Monitoring Committee shall review
each year the following data, subject to
availability, unless a TAL already has
been established for the upcoming
calendar year as part of a multiple-year
specification process, provided that new
information does not require a
modification to the multiple-year
quotas, to determine the allowable
levels of fishing and other restrictions
necessary to result in a target
exploitation rate of 23 percent (based on
Fmax) in 2003 and subsequent years:
Commercial, recreational, and research
catch data; current estimates of fishing
mortality; stock status; recent estimates
of recruitment; virtual population
analysis results; levels of
noncompliance by fishermen or
individual states; impact of size/mesh
regulations; discards; sea sampling and
winter trawl survey data, or if sea
sampling data are unavailable, length
frequency information from the winter
trawl survey and mesh selectivity
analyses; impact of gear other than otter
trawls, pots and traps on the mortality
of black sea bass; and any other relevant
information.
(b) * * *
(12) Changes, as appropriate, to the
Northeast Region SBRM, including the
CV-based performance standard, fishery
stratification, and/or reports.
*
*
*
*
*
I 14. In § 648.160, paragraph (a) is
revised and paragraph (b)(9) is added to
read as follows:
§ 648.160 Catch quotas and other
restrictions.
*
*
*
*
*
(a) Annual review. On or before
August 15 of each year, the Bluefish
Monitoring Committee will meet to
determine the total allowable level of
landings (TAL) and other restrictions
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necessary to achieve the target fishing
mortality rate (F) specified in the
Fishery Management Plan for Atlantic
Bluefish for the upcoming fishing year
or the estimated F for the fishing year
preceding the Council submission of the
recommended specifications, whichever
F is lower. In determining the TAL and
other restrictions necessary to achieve
the specified F, the Bluefish Monitoring
Committee will review the following
data, subject to availability:
Commercial, recreational, and research
catch data; current estimates of fishing
mortality; stock status; recent estimates
of recruitment; virtual population
analysis results; levels of
noncompliance by fishermen or
individual states; impact of size/mesh
regulations; discards; sea sampling data;
impact of gear other than otter trawls
and gill nets on the mortality of
bluefish; and any other relevant
information.
(b) * * *
(9) Changes, as appropriate, to the
Northeast Region SBRM, including the
CV-based performance standard, fishery
stratification, and/or reports.
*
*
*
*
*
15. In § 648.165, paragraph (a)(1) is
revised to read as follows:
I
§ 648.165
Framework specifications.
(a) * * *
(1) Adjustment process. After a
management action has been initiated,
the Council shall develop and analyze
appropriate management actions over
the span of at least two Council
meetings. The Council shall provide the
public with advance notice of the
availability of both the proposals and
the analysis and the opportunity to
comment on them prior to and at the
second Council meeting. The Council’s
recommendation on adjustments or
additions to management measures
must come from one or more of the
following categories: Minimum fish
size, maximum fish size, gear
restrictions, gear requirements or
prohibitions, permitting restrictions,
recreational possession limit,
recreational season, closed areas,
commercial season, description and
identification of essential fish habitat
(EFH), fishing gear management
measures to protect EFH, designation of
habitat areas of particular concern
within EFH, changes to the Northeast
Region SBRM (including the CV-based
performance standard, the means by
which discard data are collected/
obtained, fishery stratification, reports
and/or industry-funded observers or
observer set-aside programs), and any
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other management measures currently
included in the FMP.
*
*
*
*
*
I 16. In § 648.200, paragraph (b)
introductory text is revised to read as
follows:
§ 648.200
Specifications.
*
*
*
*
*
(b) Guidelines. As the basis for its
recommendations under paragraph (a)
of this section, the PDT shall review
available data pertaining to: Commercial
and recreational catch data; current
estimates of fishing mortality; discards;
stock status; recent estimates of
recruitment; virtual population analysis
results and other estimates of stock size;
sea sampling and trawl survey data or,
if sea sampling data are unavailable,
length frequency information from trawl
surveys; impact of other fisheries on
herring mortality; and any other
relevant information. The specifications
recommended pursuant to paragraph (a)
of this section must be consistent with
the following:
*
*
*
*
*
I 17. In § 648.206, paragraphs (b)(28)
and (b)(29) are revised and paragraph
(b)(30) is added to read as follows:
§ 648.206
Framework provisions.
*
*
*
*
*
(b) * * *
(28) TAC set-aside amounts,
provisions, adjustments;
(29) Changes, as appropriate, to the
Northeast Region SBRM, including the
CV-based performance standard, the
means by which discard data are
collected/obtained, fishery stratification,
reports, and/or industry-funded
observers or observer set-aside
programs; and
(30) Any other measure currently
included in the FMP.
*
*
*
*
*
I 18. In § 648.230, paragraphs (a), (b)(4),
and (b)(5) are revised and paragraph
(b)(6) is added to read as follows:
sroberts on PROD1PC70 with RULES
§ 648.230 Catch quotas and other
restrictions.
(a) Process for setting specifications.
The Spiny Dogfish Monitoring
Committee will review the following
data at least every 5 years, subject to
availability, to determine the total
allowable level of landings (TAL) and
other restrictions necessary to assure
that a target fishing mortality rate
specified in the Spiny Dogfish Fishery
Management Plan will not be exceeded
in each year for which TAL and any
other measures are recommended:
Commercial and recreational catch data;
discards; current estimates of F; stock
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18:32 Jan 25, 2008
Jkt 214001
status; recent estimates of recruitment;
virtual population analysis results;
levels of noncompliance by fishermen
or individual states; impact of size/mesh
regulations; sea sampling data; impact
of gear other than otter trawls and gill
nets on the mortality of spiny dogfish;
and any other relevant information.
(b) * * *
(4) Trip limits;
(5) Changes to the Northeast Region
SBRM, including the CV-based
performance standard, fishery
stratification, and/or reports; or
(6) Other gear restrictions.
*
*
*
*
*
I 19. In § 648.237, paragraph (a)(1) is
revised to read as follows:
§ 648.237
Framework provisions.
(a) * * *
(1) Adjustment process. After the
Councils initiate a management action,
they shall develop and analyze
appropriate management actions over
the span of at least two Council
meetings. The Councils shall provide
the public with advance notice of the
availability of both the proposals and
the analysis for comment prior to, and
at, the second Council meeting. The
Councils’ recommendation on
adjustments or additions to management
measures must come from one or more
of the following categories: Minimum
fish size; maximum fish size; gear
requirements, restrictions or
prohibitions (including, but not limited
to, mesh size restrictions and net limits);
regional gear restrictions; permitting
restrictions and reporting requirements;
recreational fishery measures (including
possession and size limits and season
and area restrictions); commercial
season and area restrictions; commercial
trip or possession limits; fin weight to
spiny dogfish landing weight
restrictions; onboard observer
requirements; commercial quota system
(including commercial quota allocation
procedures and possible quota setasides to mitigate bycatch, conduct
scientific research, or for other
purposes); recreational harvest limit;
annual quota specification process; FMP
Monitoring Committee composition and
process; description and identification
of essential fish habitat; description and
identification of habitat areas of
particular concern; overfishing
definition and related thresholds and
targets; regional season restrictions
(including option to split seasons);
restrictions on vessel size (length and
GRT) or shaft horsepower; target quotas;
measures to mitigate marine mammal
entanglements and interactions; regional
management; changes to the Northeast
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Fmt 4700
Sfmt 4700
4757
Region SBRM, including the CV-based
performance standard, the means by
which discard data are collected/
obtained, fishery stratification, reports,
and/or industry-funded observers or
observer set-aside program; any other
management measures currently
included in the Spiny Dogfish FMP; and
measures to regulate aquaculture
projects.
*
*
*
*
*
I 20. In § 648.260, paragraph (b)
introductory text is revised to read as
follows:
§ 648.260
Specifications.
*
*
*
*
*
(b) Development of specifications. In
developing the management measures
and specifications, the PDT shall review
at least the following data, if available:
Commercial catch data; current
estimates of fishing mortality and catchper-unit-effort (CPUE); discards; stock
status; recent estimates of recruitment;
virtual population analysis results and
other estimates of stock size; sea
sampling, port sampling, and survey
data or, if sea sampling data are
unavailable, length frequency
information from port sampling and/or
surveys; impact of other fisheries on the
mortality of red crabs; and any other
relevant information.
*
*
*
*
*
I 21. In § 648.293, paragraphs (a)(1)(xiv)
and (xv) are revised and paragraph
(a)(1)(xvi) is added to read as follows:
§ 648.293
Framework specifications.
(a) * * *
(1) * * *
(xiv) Habitat areas of particular
concern,
(xv) Set-aside quotas for scientific
research, and
(xvi) Changes to the Northeast Region
SBRM, including the CV-based
performance standard, the means by
which discard data are collected/
obtained, fishery stratification, reports,
and/or industry-funded observers or
observer set-aside programs.
*
*
*
*
*
I 22. In § 648.321, paragraphs (b)(19)
and (b)(20) are revised and paragraph
(b)(21) is added to read as follows:
§ 648.321
Framework adjustment process.
*
*
*
*
*
(b) * * *
(19) OY and/or MSY specifications;
(20) Changes to the Northeast Region
SBRM, including the CV-based
performance standard, the means by
which discard data are collected/
obtained, fishery stratification, reports,
and/or industry-funded observers or
observer set-aside programs; and
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(21) Any other measures contained in
the FMP.
*
*
*
*
*
[FR Doc. E8–1436 Filed 1–25–08; 8:45 am]
BILLING CODE 3510–22–S
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 070227048–7091–02]
RIN 0648–XF04
Magnuson-Stevens Fishery
Conservation and Management Act
Provisions; Fisheries of the
Northeastern United States; Northeast
Multispecies Fishery; Prohibition on
the Possession of Yellowtail Flounder
in the U.S./Canada Management Area
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Temporary rule; possession
prohibition.
AGENCY:
SUMMARY: NMFS announces that 100
percent of the Georges Bank (GB)
yellowtail flounder Total Allowable
Catch (TAC) has been harvested, and
that the Administrator, Northeast (NE)
Region, NMFS (Regional Administrator),
is prohibiting the harvest, possession,
and landing of GB yellowtail flounder
by all federally permitted vessels within
the entire U.S./Canada Management
Area, and maintaining the Eastern U.S./
Canada Area closure to limited access
NE multispecies days-at-sea (DAS)
vessels for the remainder of the 2007
fishing year (through April 30, 2008).
This action is being taken under the
authority of the Magnuson-Stevens
Fishery Conservation and Management
Act (Magnuson-Stevens Act), is required
by the regulations implementing
Amendment 13 to the NE Multispecies
Fishery Management Plan (FMP), and is
intended to prevent over-harvest of the
TAC for GB yellowtail flounder during
the 2007 fishing year.
DATES: Effective 0001 hours local time
January 24, 2008, through April 30,
2008.
sroberts on PROD1PC70 with RULES
FOR FURTHER INFORMATION CONTACT:
Mark Grant, Fishery Management
Specialist, (978) 281–9145, fax (978)
281–9135.
SUPPLEMENTARY INFORMATION:
Regulations governing the GB yellowtail
flounder landing limit within the U.S./
Canada Management Area are found at
VerDate Aug<31>2005
18:32 Jan 25, 2008
Jkt 214001
§ 648.85(a)(3)(iv)(C) and (D). The
regulations authorize vessels issued a
valid Federal limited access NE
multispecies permit and fishing under a
NE multispecies DAS to fish in the U.S./
Canada Management Area, as defined at
§ 648.85(a)(1), under specific
conditions. The TAC for GB yellowtail
flounder for the 2007 fishing year is 900
mt. The regulations at
§ 648.85(a)(3)(iv)(D) authorize the
Regional Administrator to increase or
decrease the trip limit in the U.S./
Canada Management Area to prevent
over-harvesting or under-harvesting the
TAC allocation . The regulations at
§ 648.85(a)(3)(iv)(C)(3) require the
Regional Administrator to prohibit the
harvesting, possession, and the landing
of GB yellowtail flounder by all
federally permitted vessels within the
entire U.S./Canada Management Area
and close the Eastern U.S./Canada Area
to all limited access NE multispecies
DAS vessels for the remainder of the
2007 fishing year when 100 percent of
the GB yellowtail flounder TAC is
projected to be caught.
Based upon the reduced 2007 TAC for
GB yellowtail flounder (a 43–percent
reduction from 2006), the GB yellowtail
flounder trip limit was initially set at
3,000 lb (1,361 kg) per trip to prevent
over-harvest during the 2007 fishing
year, and to prevent a premature closure
of the Eastern U.S./Canada Area, which
could result in reduced opportunities to
fish for GB cod and GB haddock in the
Eastern U.S./Canada Area. On
November 27, 2007, the GB yellowtail
flounder trip limit was increased to
7,500 lb (3,402 kg) because the 3,000–
lb trip (1,361–kg) limit was projected to
result in under-harvest of the TAC. The
7,500–lb (3,402–kg) trip limit resulted in
an unpredicted high rate of GB
yellowtail flounder landings, markedly
different from the historical fishing
patterns that formed the basis of the
projection. On January 10, 2008, the GB
yellowtail flounder trip limit was
decreased to 1,500 lb (680 kg) from
7,500 lb (3,402 kg) because the rapid
catch rate observed since implementing
the 7,500–lb (3,402–kg) GB yellowtail
flounder trip limit (33 percent of the
TAC was caught between December 6,
2007, and January 3, 2008) was
projected to result in the TAC being
achieved on January 23, 2008.
Based on Vessel Monitoring System
data and other available information, as
of January 17, 2008, 100 percent of the
GB yellowtail flounder TAC has been
caught. Based on this information, the
Regional Administrator, in accordance
with the regulations at
§ 648.85(a)(3)(iv)(C)(3), is prohibiting
the harvesting, possession, and the
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landing of GB yellowtail flounder by all
federally permitted vessels within the
entire U.S./Canada Management Area,
and closes the Eastern U.S./Canada Area
to all limited access NE multispecies
DAS vessels for the remainder of the
2007 fishing year effective 0001 hours
local time January 24, 2008, through
April 30, 2008.
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)(3)(B) and
(d)(3), there is good cause to waive prior
notice and opportunity for public
comment, as well as the delayed
effectiveness for this action, because
prior notice and comment, and a
delayed effectiveness, would be
impracticable and contrary to the public
interest. This action prohibits the
harvest, possession, and landing of GB
yellowtail flounder by all federally
permitted vessels within the entire U.S./
Canada Management Area and closes
the Eastern U.S./Canada Area to limited
access NE multispecies DAS vessels for
the remainder of the 2007 fishing year
(through April 30, 2008). This action is
being taken to prevent the GB yellowtail
flounder TAC from being exceeded
during the 2007 fishing year. This action
is required by the regulations at 50 CFR
648.85(a)(3)(iv)(C)(3) and is nondiscretionary. Since 100 percent of the
GB yellowtail flounder TAC is projected
to have been harvested as of January 17,
2008, there is insufficient time to allow
for public notice, comment, and delayed
effectiveness before the TAC will be
exceeded.
It was not possible to take this action
earlier to provide more time for public
comment because of the rapidly
increasing GB yellowtail flounder
harvest rate, the reduced GB yellowtail
flounder TAC, and the ability of NMFS
to monitor the harvest (the estimate that
100 percent of the GB yellowtail
flounder TAC had been harvested was
not available until January 17, 2008).
Exceeding the 2007 TAC for GB
yellowtail flounder would increase
mortality of this overfished stock
beyond that evaluated during the
development of Amendment 13 to the
FMP, resulting in decreased revenue for
the NE multispecies fishery, increased
economic impacts to vessels operating
in the U.S./Canada Management Area, a
reduced chance of achieving optimum
yield in the groundfish fishery, and
unnecessary delays to the rebuilding of
this overfished stock.
The potential of prohibiting the
harvest, possession, and landing of GB
yellowtail flounder by all federally
E:\FR\FM\28JAR1.SGM
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Agencies
[Federal Register Volume 73, Number 18 (Monday, January 28, 2008)]
[Rules and Regulations]
[Pages 4736-4758]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-1436]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 648
[Docket No. 070627217-7523-02]
RIN 0648-AV70
Magnuson-Stevens Fishery Conservation and Management Act
Provisions; Fisheries of the Northeastern United States; Northeast
Region Standardized Bycatch Reporting Methodology Omnibus Amendment
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS is implementing approved management measures contained in
the Standardized Bycatch Reporting Methodology (SBRM) Omnibus Amendment
(SBRM Amendment) to the Fishery Management Plans (FMPs) of the
Northeast Region, developed by the Mid-Atlantic and New England Fishery
Management Councils (Councils). The SBRM Amendment establishes an SBRM
for all 13 Northeast Region FMPs, as required under the Magnuson-
Stevens Fishery Conservation and Management Act (Magnuson-Stevens Act).
The measures include: Bycatch reporting and monitoring mechanisms;
analytical techniques and allocation of at-sea fisheries observers; an
SBRM performance standard; a review and reporting process; framework
adjustment and annual specifications provisions; a prioritization
process; and provisions for industry-funded observers and observer set-
aside programs.
DATES: This final rule is effective February 27, 2008.
[[Page 4737]]
ADDRESSES: Copies of the SBRM Amendment, and of the Environmental
Assessment (EA), with its associated Finding of No Significant Impact
(FONSI), and the Regulatory Impact Review (RIR), are available from
Daniel T. Furlong, Executive Director, Mid-Atlantic Fishery Management
Council, Room 2115, Federal Building, 300 South New Street, Dover, DE
19901-6790; and from Paul J. Howard, Executive Director, New England
Fishery Management Council, 50 Water Street, Newburyport, MA 01950. The
EA/FONSI/RIR is also accessible via the Internet at https://
www.nero.noaa.gov.
FOR FURTHER INFORMATION CONTACT: Michael Pentony, Senior Fishery Policy
Analyst, 978-281-9283.
SUPPLEMENTARY INFORMATION:
Background
This final rule implements approved management measures contained
in the Northeast Region Omnibus SBRM Amendment, which was approved by
NMFS on behalf of the Secretary of Commerce (Secretary) on October 22,
2007. A proposed rule for this action was published on August 21, 2007
(72 FR 46588), with public comments accepted through September 20,
2007. A subsequent publication extended this comment period through
September 24, 2007 (72 FR 53751).
Section 303(a)(11) of the Magnuson-Stevens Act requires that all
FMPs ``establish a standardized reporting methodology to assess the
amount and type of bycatch occurring in the fishery.'' In 2004, several
conservation organizations challenged the approval of two major
amendments to Northeast Region FMPs. In ruling on these suits, the U.S.
District Court for the District of Columbia found that the FMPs did not
clearly establish an SBRM as required under the relevant section of the
Magnuson-Stevens Act and remanded the amendments back to the agency to
fully develop and establish the required SBRM [See, Oceana, Inc., v.
Evans, 2005, WL 555416 (D.D.C. Mar 9, 2005)(Oceana I); and Oceana,
Inc., v. Evans, 384 F. Supp 2d 203 (D.D.C. 2005)(Oceana II)]. In
particular, the Court found that the amendments (1) failed to fully
evaluate reporting methodologies to assess bycatch, (2) did not mandate
an SBRM, and (3) failed to respond to potentially important scientific
evidence.
In response, the Councils, working closely with NMFS, undertook
development of a remedy that would address all Northeast Region FMPs.
In January 2006, development began on the Northeast Region Omnibus SBRM
Amendment. This amendment covers 13 FMPs, 39 managed species, and 14
types of fishing gear. The purpose of the amendment is to: Explain the
methods and processes by which bycatch is currently monitored and
assessed for Northeast Region fisheries; determine whether these
methods and processes need to be modified and/or supplemented;
establish standards of precision for bycatch estimation for all
Northeast Region fisheries; and, thereby, document the SBRM established
for all fisheries managed through the FMPs of the Northeast Region. The
amendment also responds to the ``potentially important scientific
evidence'' cited by the Court in the two decisions referenced above.
The Northeast Region SBRM Amendment establishes an SBRM comprised
of seven elements: (1) The methods by which data and information on
discards are collected and obtained; (2) the methods by which the data
obtained through the mechanisms identified in element 1 are analyzed
and utilized to determine the appropriate allocation of at-sea
observers; (3) a performance measure by which the effectiveness of the
Northeast Region SBRM can be measured, tracked, and utilized to
effectively allocate the appropriate number of observer sea days; (4) a
process to provide the Councils with periodic reports on discards
occurring in Northeast Region fisheries and on the effectiveness of the
SBRM; (5) a measure to enable the Councils to make changes to the SBRM
through framework adjustments and/or annual specification packages
rather than full FMP amendments; (6) a process to provide the Councils
and the public with an opportunity to consider, and provide input into,
the decisions regarding prioritization of at-sea observer coverage
allocations; and (7) to implement consistent, cross-cutting observer
service provider approval and certification procedures and to enable
the Councils to implement either a requirement for industry-funded
observers or an observer set-aside program through a framework
adjustment rather than an FMP amendment.
Bycatch Reporting and Monitoring Mechanisms
The amendment maintains the status quo methods by which data and
information on discards occurring in Northeast Region fisheries are
collected and obtained. The Northeast Region SBRM will employ sampling
designs developed to minimize bias to the maximum extent practicable.
The Northeast Fisheries Observer Program (NEFOP) continues to serve as
the primary mechanism to obtain data on discards in all Northeast
Region commercial fisheries managed under one or more of the subject
FMPs. All subject FMPs will continue to require vessels permitted to
participate in said fisheries to carry an at-sea observer upon request,
and all data obtained by the NEFOP under this SBRM will be collected
according to the techniques and protocols established and detailed in
the Fisheries Observer Program Manual and the Biological Sampling
Manual. Data collected by the NEFOP include, but are not limited to,
the following items: Vessel name; date/time sailed; date/time landed;
steam time; crew size; home port; port landed; dealer name; fishing
vessel trip report (FVTR) serial number; gear type(s) used; number/
amount of gear; number of hauls; weather; location of each haul
(beginning and ending latitude and longitude); species caught;
disposition (kept/discarded); reason for discards; and weight of catch.
These data are collected on all species of biological organisms caught
by the fishing vessel and brought on board, including species managed
under the subject FMPs, but also including species of non-managed fish,
invertebrates, and marine plants. To obtain information on discards
occurring in recreational fisheries subject to a Northeast Region FMP,
the Northeast Region SBRM fully will incorporate, to the extent
practicable and appropriate for the Region, all surveys and data
collection mechanisms implemented by NMFS and affected states as a
result of the agency-wide redesign of the Marine Recreational Fisheries
Statistics Survey (MRFSS) Program.
Analytical Techniques and Allocation of At-sea Fisheries Observers
The amendment substantially expands and refines the status quo
methods by which the data obtained through the mechanisms included
above are analyzed and utilized to determine the appropriate allocation
of at-sea observers to fully incorporate all managed species and all
relevant fishing gear types in the Northeast Region. At-sea fisheries
observers will, to the maximum extent possible and subject to available
resources, be allocated and assigned to fishing vessels according to
the procedures established through the amendment. All appropriate
filters identified in the amendment will be applied to the results of
the analysis to determine the observer coverage levels needed to
achieve the objectives of the SBRM.
[[Page 4738]]
SBRM Performance Standard
The amendment is intended to ensure that the data collected under
the Northeast Region SBRM are sufficient to produce a coefficient of
variation (CV) of the discard estimate of no more than 30 percent, in
order to ensure that the effectiveness of the Northeast Region SBRM can
be measured, tracked, and utilized to effectively allocate the
appropriate number of observer sea days. Each year, the Regional
Administrator and the Science and Research Director will, subject to
any external operational constraints, allocate at-sea observer coverage
to the applicable fisheries of the Northeast Region sufficient to
achieve a level of precision (measured as the CV) no greater than 30
percent for each applicable species and/or species group, subject to
the use of the filters noted above.
SBRM Review and Reporting Process
The amendment requires an annual report on discards occurring in
Northeast Region fisheries to be prepared by NMFS and provided to the
Councils, and a report every 3 years that evaluates the effectiveness
of the Northeast Region SBRM. Every 3 years, the Regional Administrator
and the Science and Research Director will appoint appropriate staff to
work with staff appointed by the Executive Directors of the Councils to
obtain and review available data on discards and to prepare a report
assessing the effectiveness of the Northeast Region SBRM. This report
will include, at a minimum: (1) A review of the recent levels of
observer coverage in each applicable fishery; (2) a review of recent
observed encounters with each species in each fishery, and a summary of
observed discards by weight; a review of the CV of the discard
information collected for each fishery; (4) an estimate of the total
discards associated with each fishery; (5) an evaluation of the
effectiveness of the SBRM at meeting the performance standard for each
fishery; (6) a description of the methods used to calculate the
reported CVs and to determine observer coverage levels, if those
methods are different from those described and evaluated in the SBRM
Amendment; (7) an updated assessment of potential sources of bias in
the sampling program and analyses of accuracy; and (8) an evaluation of
the implications for management of the discard information collected
under the SBRM, for any cases in which the evaluation performed for
item 5 indicates that the performance standard is not met. Once each
year, the Science and Research Director will present to the Councils a
report on catch and discards occurring in Northeast Region fisheries,
as reported to the NEFOP by at-sea fisheries observers. This annual
discard report will include: (1) The number of observer sea days
scheduled for each fishery, by area and gear type, in each quarter; (2)
the percent of total trips observed, by gear type, in each quarter; (3)
the distribution of sea sampling trips by gear type and statistical
area in each fishery; (4) the observed catch and discards of each
species, by gear type and fishery, in each quarter; and (5) the
observed catch and discards of each species, by gear type and fishery,
in each statistical area.
Framework Adjustment and/or Annual Specification Provisions
The amendment enables the Councils to make changes to certain
elements of the SBRM through framework adjustments and/or annual
specification packages rather than full FMP amendments. All subject
FMPs provide for an efficient process to modify aspects of the
Northeast Region SBRM, as relates to each specific FMP, should the need
arise and the appropriate Council determine that a change to the SBRM
is warranted and needed to address a contemporary management or
scientific issue. Depending on the provisions of each FMP, changes to
the SBRM may be effected either through a framework adjustment to the
FMP or through annual or periodic specifications. Such changes to the
SBRM may include modifications to the CV-based performance standard,
the means by which discard data are collected/obtained in the fishery,
reporting on discards or the SBRM, or the stratification (modes) used
as the basis for SBRM-related analyses. Such changes may also include
the establishment of a requirement for industry-funded observers and/or
observer set-aside provisions.
Prioritization Process
The amendment establishes a process to provide the Councils and the
public with an opportunity to consider, and provide input into, the
decisions regarding prioritization of at-sea observer coverage
allocations, if the expected resources necessary may not be available.
In any year in which external operational constraints would prevent
NMFS from fully implementing the required at-sea observer coverage
levels, the Regional Administrator and Science and Research Director
will consult with the Councils to determine the most appropriate
prioritization for how the available resources should be allocated. In
order to facilitate this consultation, in these years, the Regional
Administrator and the Science and Research Director will provide the
Councils, at the earliest practicable opportunity: (1) The at-sea
observer coverage levels required to attain the SBRM performance
standard in each applicable fishery; (2) the coverage levels that would
be available if the resource shortfall were allocated proportionately
across all applicable fisheries; (3) the coverage levels that
incorporate the recommended prioritization; and (4) the rationale for
the recommended prioritization. The recommended prioritization should
be based on: Meeting the data needs of upcoming stock assessments;
legal mandates of the agency under other applicable laws, such as the
Marine Mammal Protection Act (MMPA) and the Endangered Species Act
(ESA); meeting the data needs of upcoming fishery management actions,
taking into account the status of each fishery resource; improving the
quality of discard data across all fishing modes; and/or any other
criteria identified by NMFS and/or the Councils. The Councils may
choose to accept the proposed observer coverage allocation or to
recommend revisions or additional considerations for the prioritized
observer allocations ultimately adopted and implemented by the Regional
Administrator and the Science and Research Director.
Industry-Funded Observers and Observer Set-Aside Program Provisions
The amendment implements consistent, cross-cutting observer service
provider approval and certification procedures and enables the Councils
to implement either a requirement for industry-funded observers and/or
an observer set-aside program through a framework adjustment, rather
than an FMP amendment.
Comments and Responses
A total of 11 individual comment letters were received on the
proposed rule and the amendment.
Comment 1: A letter by representatives of a professional
association for at-sea fisheries observers raised concerns regarding
the provision of the SBRM Amendment that establishes observer
certification and approval procedures to allow a multiple service
delivery model under an industry-funded observer program. The
commenters specifically focused on concerns related to the contractual
relationship that would be established between the observer service
provider
[[Page 4739]]
and the fishing vessel, rather than between the observer service
provider and NMFS. The commenters refer to experience with a similar
model utilized in Alaska under the North Pacific Groundfish Observer
Program. The commenters cautioned that, in their opinion, such a
contractual relationship may reduce the reliability of the data
collected by the at-sea observers due to the potential for bias and
conflict of interest. The commenters also cited concerns over quality
control of the data due to the lack of direct oversight by the agency.
To remedy the potential problems they identified, the commenters
suggested that NMFS evaluate the performance of approved observer
service providers on an annual basis, increase Federal funding for
observers contracted by and paid for by NMFS, and/or utilize an
independent non-profit organization (either an existing organization
such as the Atlantic States Marine Fisheries Commission or an
organization created specifically for this purpose) to provide an
``arms-length'' relationship between the fishing industry, NMFS, and
observer service providers.
Response: NMFS acknowledges that a perceived conflict of interest
could be a potential issue for some types of industry-funded observer
programs. Rigorous data quality assurance and control standards,
observer training and certification programs, and frequent reviews and
oversight of the observer data collection programs are all means to
address these concerns. NMFS acknowledges that some of the issues
raised by the commenter regarding the North Pacific Groundfish Observer
Program have been previously identified as potential concerns with that
model, but notes that there are significant differences between the
North Pacific program and the single industry-funded program that is
currently in place in the Northeast Region. These differences include
the observer set-aside that is an important component of the Northeast
sea scallop observer program and serves to mitigate the conflict of
interest concerns by providing a mechanism to offset the added cost to
sea scallop fishing vessels of carrying an observer. Also, to minimize
the likelihood that an observer would develop ties to a vessel owner/
operator and/or feel pressure by a vessel owner/operator to misreport,
the regulations prohibit observer service providers from consecutively
deploying the same observer on the same vessel and from deploying an
observer on the same vessel more than twice per month.
While NMFS shares some of the concerns identified by the commenters
relative to the need to ensure that there is no real or perceived
conflict of interest between the at-sea observers and the fishing
vessels, and to ensure reliable, high quality data are collected and
reported, none of these concerns are immediately applicable to this
rulemaking. The regulatory changes implemented in this final rule
merely establish the procedures that potential observer service
providers must follow to be considered for approval, and the standards
that they must meet on a continuing basis to maintain their
certification to serve in the Northeast Region. However, excepting the
sea scallop observer program that was formally implemented under a
separate rulemaking (72 FR 32549, June 13, 2007), no other fisheries in
the Northeast Region are operating under an industry-funded observer
requirement that would utilize these regulations. This action makes no
changes to the regulations or procedures established under Amendment 13
to the Sea Scallop FMP, other than to generalize the observer
certification procedures to apply more broadly than for the sea scallop
fishery alone. The intent of this action was to create a more efficient
process for the Councils to develop future industry-funded programs,
should the need arise in any fishery. Actual implementation of an
industry-funded observer program that would enable fishing vessels to
select from a list of approved observer service providers would require
the appropriate Council to initiate, develop, and have approved such a
program for each particular fishery.
The development of future Council fishery management actions to
implement any additional industry-funded observer programs provides the
appropriate opportunity to ensure that the programs fully address the
data quality concerns and limitations noted by the commenters. NMFS is
committed to ensuring that data collected and provided by at-sea
fisheries observers are of the highest-possible quality and meet all
applicable standards for reliability, precision, and accuracy. Any
proposal by a Council to implement a future industry-funded observer
program, such as is currently in place for the sea scallop fishery,
would be reviewed to ensure it fully explains and justifies how the
data to be obtained through the program meet all appropriate quality
standards.
Comment 2: One member of the public endorsed the comments of the
observers' professional association, voicing his concern over industry-
funded observer programs as exist in Alaska under the North Pacific
Groundfish Observer Program. The commenter added, however, that his
concerns do not refer to the sea scallop observer program that is
linked to an observer set-aside program to offset the costs to the
vessels of carrying an observer. The commenter is most concerned with
the perceptions of conflict of interest that can arise under situations
where the observer service provider is contractually linked, and
dependent on, the fishing vessels rather than NMFS.
Response: The response above to comment 1 addresses the majority of
the points raised by the commenter. As noted by the commenter, observer
set-aside programs, such as the Northeast sea scallop program, mitigate
many of these concerns by providing a mechanism to offset the added
cost to the vessel of carrying an observer. While there is no
requirement to do so, NMFS fully anticipates that any program developed
by a Council to implement an industry-funded observer program would be
directly associated with an observer set-aside program that offsets the
additional costs to the vessels. No such program is currently proposed
or under development by either Council, but the SBRM Amendment provides
a mechanism for the Councils to develop and propose a set-aside program
that uses quota, days-at-sea, increased trip limits, or other means to
compensate fishing vessels that carry observers.
Comment 3: The comments submitted by a public interest
environmental organization were very similar to those of the observers'
professional association. The commenters oppose changing the NEFOP to a
model based on the North Pacific Groundfish Observer Program, in which
the industry finances the observer program through independent
contracts with observer service providers. The commenters raised
concerns regarding the appearance of a conflict of interest between the
fishing vessels and the observer service providers, a threat of bias in
the data collection, creating an economic incentive to avoid
observation, less transparency of observer data, and a lack of control
on harassment of an interference with observers. The comment letter
also expressed concern that the SBRM would discourage monitoring for
marine mammals and other non-bycatch related monitoring.
Response: Although the commenters in this case appear to have
misunderstood the intent of the SBRM Amendment, NMFS takes their
concerns seriously. The response above to comment 1 addresses the
majority of the concerns raised by the commenters, but NMFS points out
that the commenters
[[Page 4740]]
claim that the SBRM Amendment effects a ``conversion'' of the NEFOP
from one controlled by NMFS to an industry-funded program. This is not
the case. The SBRM Amendment provides a mechanism for the Councils to
develop and propose industry-funded observer programs that would serve
to supplement the existing NMFS-funded observer program, but this
action neither implements nor requires such a program. Currently, the
Councils are free to develop and propose such a system (as was done in
Amendment 13 to the Sea Scallop FMP); the SBRM Amendment allows the
Councils to use the framework adjustment process to propose a similar
program instead of requiring a full FMP amendment. NMFS fully
anticipates that any such program would include an observer set-aside
mechanism, such as exists for the sea scallop fishery. As noted above
and by other commenters, such a mechanism mitigates many of the
concerns raised by the commenters.
NMFS disagrees with the commenter that such a system, should one be
proposed by a Council and implemented by NMFS, would result in industry
``control'' of the observer program. The regulations at 50 CFR
648.11(h) and (i) provide extensive and detailed procedures that must
be followed by all observer service providers in order to obtain and
maintain NMFS certification as valid service providers. These
regulations specifically address the issues of potential conflicts of
interest (Sec. 648.11(h)(6)), harassment of or interference with
observers (Sec. 648.11(h)(5)(vii)(F)), and data transparency (Sec.
648.11(h)(5)(vii)(A)). Regarding the concerns raised about the
availability of the ``raw'' observer data, the regulations at Sec.
648.11(h)(5)(vii)(A) require that, in addition to providing summary
data within 12 hours of landing, that the observer service providers
``provide the raw (unedited) data collected by the observer to NMFS
within 72 hours of the trip landing.'' Regarding the commenters'
opinion that the plan creates an economic incentive to evade
observation, this claim does not take into account that observer set-
aside programs in many ways may actually create an incentive to be
observed, as a set-aside program would grant a vessel extra quota,
trips, DAS, or increased possession limits in exchange for carrying an
observer.
The commenters are also incorrect that the plan ``discourages''
marine mammal monitoring. NMFS acknowledges in the SBRM Amendment the
importance of its mandate under other applicable laws, such as the MMPA
and the Migratory Bird Act, but the focus of the SBRM is on those
living marine resources defined as fish and bycatch under the Magnuson-
Stevens Act. Only the Magnuson-Stevens Act requires an SBRM to be
established, and the Magnuson-Stevens Act specifically excludes certain
types of organisms, specifically marine mammals and birds, from the
definitions.
The commenters are mistaken to conclude that the ``SBRM is based on
a flawed model.'' The actual SBRM established as a result of this
action is wholly severable from the provision that authorizes the
Councils to develop and propose an industry-funded observer program
through a framework adjustment rather than an amendment to an FMP. The
SBRM does not implement, require, or rely upon any industry-funded
observer programs that may be developed and proposed by a Council in
the future.
Comment 4: An organization representing a coalition of fishing
interests involved in the Atlantic herring fishery submitted comments
critical of the field sampling protocols and procedures used by at-sea
observers to monitor bycatch occurring in fisheries that pump their
catch directly from the codend into the vessel hold. The commenters
asserted that the current observer protocols for the herring fishery
contain loopholes that were not addressed in the SBRM Amendment, due to
the potential for unobserved catch to be released from the net without
being brought on board the vessel for the observer to monitor. The
commenters expressed concern regarding the lack of mandated observer
coverage on at-sea processing vessels, which transfer catch from the
codend of catcher vessels to the hold of the processor vessel and about
how pair trawls are treated if an observer is aboard only one of the
paired vessels. The commenters also expressed concern that the
filtering procedures described in the SBRM Amendment would result in
exclusion of certain fishing modes (such as mid-water trawls) from
observer coverage due to low levels of coverage in the past (``the SBRM
ensures that [the mid-water trawl] mode will be unobserved in
perpetuity'').
Response: All fishing vessels permitted by NMFS to operate in the
Northeast Region under one or more of the FMPs subject to the SBRM
Amendment are currently obligated to carry a NMFS-certified observer on
any trip for which they are requested by the Regional Administrator to
do so (at Sec. 648(a), (b), (c) , and (d)). This requirement does not
change, and is, in fact, reinforced in section 1.7 of the amendment.
This requirement, by definition, applies to herring at-sea processors.
The commenters incorrectly claim that the SBRM excludes some fishing
modes from observer coverage; in fact, according to the results of the
importance filter adopted in the amendment, the coverage allocated to
the New England mid-water trawl fishing mode, cited by the commenters
as ``unobserved in perpetuity,'' would be 316 days, nearly twice the
coverage level in 2004 and would represent 11.5 percent of trips taken
in 2004. The commenters appear to misunderstand the function of the
importance filters, which is to eliminate certain species (those for
which the total discards in a fishing mode is a negligible proportion
of either the total discards of that species across all fishing modes,
or for which the total discards of that species is a negligible
proportion of total fishing-related mortality of that species) from the
calculation of the observer coverage allocation within a fishing mode
(the allocation being no less than the highest coverage level of all
species remaining after the importance filter is applied). Under no
circumstances do the importance filters eliminate any fishing modes
from the observer allocation process. This can be seen in Appendix C of
the amendment in a table illustrating the results of applying the SBRM
to the 2004 dataset. There is some level of observer coverage assigned
to each of the 39 fishing modes addressed in the SBRM Amendment. In
addition, the commenters asserted that the SBRM Amendment did not
address the field sampling protocols to be used in collecting data by
at-sea fisheries observers. This is incorrect. Section 1.7 of the SBRM
Amendment stipulates that ``The NEFOP shall serve as the primary
mechanism to obtain data on discards in all Northeast Region commercial
fisheries managed under one or more of the subject FMPs,'' and that
``all data obtained by the NEFOP under this SBRM shall be collected
according to the techniques and protocols established and detailed in
the Fisheries Observer Program Manual (NEFOP 2006a) and the Biological
Sampling Manual (NEFOP 2006b).'' This section of the SBRM Amendment
goes on to identify the minimum data fields to be collected by
Northeast Region observers. The Fisheries Observer Program Manual and
the Biological Sampling Manual provide general as well as specific
instructions for at-sea observers operating on mid-water trawl, purse
seine, and pair trawl vessels; these instructions and sampling
priorities explicitly account, to the extent
[[Page 4741]]
practicable, for the contingencies identified by the commenters
(including pair trawls with only one vessel observed, pumped fish, loss
of fish in the net, etc.).
Comment 5: A letter from an organization representing commercial
fishermen from Cape Cod expressed concern with how the SBRM would
perform in monitoring hard TACs (total allowable catch) and fishery
sectors. The commenters acknowledged that at least some of the changes
under the SBRM Amendment will improve the region's bycatch reporting,
and characterized the importance filter process as ``crucial for
prioritizing observer coverage.'' However, the commenters stressed
three primary recommendations for improving the SBRM Amendment: (1)
Ensuring that the SBRM provides a means to accurately and precisely
quantify discards for all stocks across all stock areas; (2)
identifying levels of monitoring coverage for sectors necessary for TAC
management; and (3) providing a real-time, publicly-accessible, and
transparent reporting methodology that allows for enforcement of
accountability measures.
Response: The commenters imply that the SBRM Amendment should have
addressed the new requirement included in the Magnuson-Stevens
Reauthorization Act of 2007 (MSRA) for all FMPs to include ``Annual
Catch Limits'' (ACLs) and ``Accountability Measures'' (AMs) and
indicate how the SBRM would perform in the face of these new
requirements. However, the MSRA does not require ACLs and AMs be
developed and implemented for any fishery until at least 2010 (for
fisheries experiencing overfishing) or 2011 (for all other fisheries).
Also, the new MSRA provision related to ACLs and AMs, by its very
definition, applies to all catch, not just bycatch, and is a
requirement much broader in scope than the requirement to establish an
SBRM, which remains a separate requirement under the Magnuson-Stevens
Act and was not modified by the MSRA. Section 1.2 of the SBRM Amendment
acknowledges the changes promulgated through the MSRA, but explains
that no changes to the amendment are necessary as a result. This action
remains necessary primarily to correct deficiencies identified by the
Court in Amendment 13 to the Northeast Multispecies FMP and Amendment
10 to the Sea Scallop FMP in order to bring the Northeast Region FMPs
into compliance with the requirement to establish an SBRM as specified
as section 303(a)(11) of the Magnuson-Stevens Act. As the Councils
embark on fishery management actions to bring the FMPs into compliance
with the new requirements of the MSRA, changes to the SBRM established
herein may be necessary to accommodate the specific attributes of the
ACLs and AMs that will be developed, but such changes would address
specific management needs that go beyond the mandate of section
303(a)(11) to establish an SBRM to assess the amount and type of
bycatch, which is the focus of this action. Because it is impossible at
this time to foresee all the particular attributes of the various ACL
and AM programs that may be developed and adopted by the two Councils
for all 13 FMPs, and how the SBRM may need to change to accommodate
those programs, it would be premature to attempt to craft an SBRM that
could accommodate all possible ACL and AM outcomes, without resulting
in an SBRM so vague and generalized as to be ineffectual at meeting its
current objectives.
Regarding the specific points raised by the commenter, NMFS asserts
that the Northeast Region SBRM is wholly sufficient to quantify
discards for all stocks across all stock areas. Data collected by at-
sea fisheries observers provide sufficient information to determine the
specific stocks of fish discarded, and the stock areas in which the
discard event occurred. These data can be used to apportion the
collected discard estimates across all stocks and stock areas. This is
illustrated in Appendix F and Appendix G of the amendment, which
provide example data queries and analyses based on the data collected
by at-sea observers and a sample format for the information requested
by the Councils to be provided in annual discard reports. In both
cases, discard data are summarized by stock and statistical area, which
is a finer scale even than stock area (i.e., stock areas are composed
of multiple statistical areas).
The commenters also suggest that the SBRM must identify observer
coverage levels for fishery sectors authorized under an FMP to provide
for a specific level of certainty in future TAC management programs.
The commenters appear to assume that a one-size-fits-all approach would
be appropriate for all potential future instances of sector management.
Sectors are unique and temporary fishery management provisions that
authorize a collective of similar fishing vessels (e.g., hook vessels
operating out of Cape Cod) to be granted a portion of a TAC for 1 year
in exchange for abiding by the specific provisions and limitations
identified in the sector management plan. Currently, there are two
approved sectors operating in New England waters; both are authorized
under the sector management provisions of Amendment 13 to the Northeast
Multispecies FMP. As many as 19 additional multispecies sectors are
under development, and the New England Council is considering adopting
similar sector provisions in upcoming amendments to the other New
England FMPs. The sector provisions of the Northeast Multispecies FMP
require that the vessels interested in forming a sector prepare and
submit annually a sector proposal that includes, among other things,
``detailed plans for the monitoring and reporting of landings and
discards'' (at Sec. 648.87(b)(2)(vi)). Under the sector provisions of
the FMP, it is the responsibility of the sector proponents to propose
how discards will be monitored and reported, while the Council and NMFS
retain the authority to determine if the proposed plans are sufficient.
Sector proposals developed by members of the fishing industry are
submitted to and reviewed by the New England Council. Those approved by
the Council are incorporated into framework adjustments to the
Northeast Multispecies FMP and submitted to NMFS for review. At that
time, NMFS considers the specific provisions of the proposed sector
plan to ensure it would meet all requirements of the FMP and be
consistent with the provisions of the Magnuson-Stevens Act and other
applicable law. Given the variety of sector proposals currently under
development, and the expectation of additional sector provisions
included in the other New England FMPs, it would not be practicable to
stipulate in this amendment the specific levels of observer coverage
that would be necessary for each sector, as this would depend on the
number of vessels participating, the area(s) to be fished, the target
and likely incidental species, fishing gear(s) used, and the other
reporting mechanisms required under each sector plan. This action is
focused on the requirement at section 303(a)(11) of the Magnuson-
Stevens Act to develop a methodology to assess the amount and type of
bycatch and provides a framework for modifications to the overarching
methodology to address specific future management needs. The Councils
recognized the need for the SBRM Amendment to be flexible enough to
adapt to such changes, noting in section 6.9.5 of the amendment that
because new sector programs may be implemented through a framework
adjustment, the same framework action could be used to ``modify the
SBRM to
[[Page 4742]]
ensure sufficient data are collected'' on discards.
The commenters asserted that the SBRM must establish a ``real-time,
publicly-accessible, and transparent reporting methodology.'' NMFS
disagrees with the commenters on this point. The Magnuson-Stevens Act
requires simply that an SBRM be established; it imposes no minimum
legal requirements on whether this system provide data in real time, or
the degree to which the data are publicly accessible. A ``real-time''
reporting system, as requested by the commenters, would require that
data be presented in a publicly accessible medium as the discards are
observed and documented by the at-sea fisheries observer. This would
provide no time for the fishing trip to end, for the observer to submit
the data to NMFS, and for NMFS to review, edit, and audit the data
prior to publishing the data. This would severely reduce the quality of
the data and, in so doing, diminish the usefulness and reliability of
the discard data. Data reduction and summaries are necessary in order
to prevent the release of sensitive and proprietary data that is
protected under the Magnuson-Stevens Act and other Federal statutes.
NMFS concludes that it is more appropriate to engage a full data
quality control and assurance program, as summarized in Appendix D of
the SBRM Amendment, in order to ensure the resulting data are of the
highest possible quality before they are released to the public or used
in management.
Comment 6: A conservation organization submitted extensive comments
on the SBRM Amendment and its proposed rule, urging that NMFS not
approve the amendment. The comments addressed several elements of the
SBRM Amendment, and include references to the results of a technical
review of the amendment conducted under contract to another
conservation organization. The responses to the comments identified in
the technical review are addressed separately under comment 10. All
other points raised in the comment letter are addressed in this
response.
The commenters, while acknowledging that the SBRM Amendment
``dramatically'' improves upon prior documents by specifying a
monitoring and reporting system that could be implemented, expressed
concern that the amendment fails to actually establish this system
because it vests NMFS with discretion as to the allocation of observer
coverage if there are external constraints (such as an insufficient
budget) that prevent full implementation. The commenters suggested that
the amendment could have adopted a formal decision procedure that would
stipulate how observers are to be allocated if there is a budget
shortfall, such as requiring that the budget allocations be cut pro
rata across all fishing modes, or to rank fishing modes according to a
standard of priority and fully allocating observer coverage across
priority modes until funding is exhausted.
The commenters claim that the SBRM Amendment fails to mandate that
data be reported in a rational manner useful for fisheries management,
and that the amendment fails to establish a reporting requirement that
provides information on the amount, type, and disposition of bycatch.
The commenters also claim that the amendment fails to recognize the
fishery management needs of the Councils and the needs of the public.
The commenters claim that the amendment fails to establish an SBRM
because it provides for framework adjustment provisions to enable the
Councils to develop and propose changes to the SBRM. The commenters
also claim that the SBRM Amendment fails to consider the bycatch of
species that are not targeted under Northeast Region FMPs, including
failing to consider alternatives for including ``non-managed'' species
in the SBRM.
The commenters claim that NMFS ``locked'' the public and Fishery
Management Councils out of the decision-making process to develop the
SBRM Amendment. The commenters also claim that the SBRM Amendment
violates NEPA because an environmental impact statement (EIS) was not
prepared. Regarding the environmental assessment's (EA) compliance with
NEPA, the commenters raised the following concerns: The EA fails to
adequately discuss the purpose, need, and scope of the amendment; the
EA fails to consider a reasonable range of alternatives, including
performance standards other than 30 percent, different reporting
formats or frequencies, or different ways to assess accuracy; the EA
fails to consider cumulative environmental impacts; and the EA fails to
adequately address protected resources.
Response: NMFS disagrees with the commenters' assertion that the
amendment fails to establish an SBRM because it vests NMFS with some
degree of discretion in cases where external operational constraints
prevent full implementation of the resulting at-sea observer
allocations. The SBRM Amendment establishes an extensive and detailed
methodology to utilize available observer data on discards occurring
across all relevant Northeast Region fisheries, assess the degree to
which those data meet the established performance standard, allocate
observer coverage levels across all relevant fisheries to achieve said
performance standard, and provide reports to the Fishery Management
Councils on the discards that are occurring and on the effectiveness of
the SBRM itself at meeting its objectives. The prioritization process
is one component of the overall program that explicitly recognizes that
external operational constraints (such as Congressional budget
allocations) may occasionally prevent the full implementation of the
SBRM. The process establishes a rigorous review and consultation
process to engage the Councils and the public in determining the most
appropriate approach to prioritize observer coverage on these occasions
that reflects the needs and priorities of the agency and Councils at
the time.
The commenters suggested that the amendment could have implemented
a requirement to apportion any budget allocations pro rata across all
fishing modes, or could have ranked fishing modes according to a
specific standard of priority and require that observers be fully
allocated to the highest priority modes in descending order until the
available budget is exhausted. NMFS notes that several options such as
these are described in section 6.6 of the amendment, but that the
Councils recognized the importance of retaining sufficient flexibility
in the SBRM to adapt to changing conditions and priorities in the
fisheries. The approach suggested by the commenters would leave the
Councils and NMFS with a rigid system that would require an FMP
amendment to modify the priority allocation of resources. NMFS also
notes that retaining some level of discretion in allocating resources
is necessary for the agency to adequately meet its obligations under
other laws in addition to the Magnuson-Stevens Act, such as the ESA and
MMPA. Lastly, the commenters appeared to have misconstrued the
instructions from the Court. Instead of requiring that the SBRM
Amendment stipulate the precise areas where observers must be
concentrated, the Court, in Oceana II, clarified that it ``only
requires that the FMP establish some method for determining observer
concentration instead of leaving all decisions to the Regional
Administrator's discretion'' [See, Oceana II at p. 234 (footnote 41)].
The SBRM Amendment establishes a very specific method for determining
observer allocations across all relevant fisheries, and does not leave
``all
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decisions'' to the Regional Administrator. Rather, only in years in
which external operational constraints prevent full implementation
would NMFS have any discretion to adapt the results of the SBRM, and
only then following a review and consultation with the Councils in a
public forum. NMFS asserts that this approach is consistent with both
the intent of the SBRM provisions of the Magnuson-Stevens Act and the
guidance provided by the Court.
NMFS rejects the commenters' claim that the SBRM Amendment fails to
mandate that data be reported in a rational manner useful for fisheries
management, and that the amendment fails to establish a reporting
requirement that provides information on the amount, type, and
disposition of bycatch. Section 6.4 of the SBRM Amendment describes the
alternatives considered regarding potential reporting procedures, and
section 1.7 of the amendment establishes the requirements for two types
of reports to be prepared at different time intervals. The amendment
requires an annual report be provided to the Councils to provide the
data they requested on the current status of observer coverage and
discard information, along with an additional report provided every 3
years that assesses the SBRM in a more comprehensive manner. The
amendment, in sections 1.7 and 6.4, identifies the specific data
elements to be provided in the reports, including the amount, species,
location, and gear types involved. The information to be reported, the
frequency, and the format for the reports was proposed and adopted by
both Councils as their preferred alternative approach to obtaining SBRM
reports on a routine basis. NMFS asserts that the Councils are in the
best position to determine their needs as to SBRM reports, and, as
such, the SBRM Amendment clearly reflects the needs of the Councils for
this information.
NMFS disagrees with the commenters that the SBRM Amendment fails to
actually establish an SBRM simply because it provides a procedure for
the Councils to make changes to certain provisions of the SBRM through
the use of framework adjustments rather than full FMP amendments. The
intent of this provision of the amendment is to facilitate an efficient
and timely process for the Councils to develop and submit proposed
changes to the SBRM, limited within certain constraints. Nothing in
this provision diminishes or abrogates the agency's obligation to
carefully review any framework adjustment proposed by a Council to
ensure that the proposed changes are consistent with the Magnuson-
Stevens Act, other applicable law, and do not undermine or contravene
the parent FMP. The amendment clearly stipulates that intent, as at
section 6.5.2, which provides that ``the intent of this [framework]
provision is to provide an efficient means for the Council to change
the performance standard in certain circumstances when a higher level
of precision (i.e., reducing the CV to less than 30 percent) is desired
for a particular fishery or management program [emphasis added].''
Providing this mechanism to modify certain elements of the SBRM is
considered important because several provisions of the parent FMPs
already establish framework adjustment protocols for items such as
creating new special access programs (SAPs) or new fishery sectors. As
these changes are developed through a framework adjustment process,
changes to the SBRM may be necessary in order to ensure sufficient
discard reporting in the new SAP or sector. Without the ability to
effect the necessary changes to the SBRM through the framework
adjustment implementing the SAP or sector, the Council would have to
defer implementation of each such framework until an accompanying
amendment could be developed to implement the changes to the SBRM. This
delay would directly contravene the intent of the parent FMPs.
NMFS also disagrees with the commenters that the amendment failed
to consider the bycatch of species that are not targeted under the
Northeast Region FMPs. This issue is addressed in several sections of
the amendment. First, section 1.7 of the amendment clearly stipulates
that the data collected by at-sea fisheries observers ``shall be
collected on all species of biological organisms caught by the fishing
vessel and brought on board, including species managed under the
subject FMPs but also including species on non-managed fish,
invertebrates, and marine plants.'' This section of the amendment
continues to stipulate, in a footnote, that a complete list of the
species for which the listed data elements are to be collected can be
found in Appendix A and Appendix R of the Fisheries Observer Program
Manual. These lists include more than 500 distinct species and species
codes that must be accounted for by observers in their catch and
discard reports. This provision of the SBRM requires that information
regarding the discards of all species be reported by at-sea observers
and reported to NMFS. The same information collected on species managed
under a subject Northeast Region FMP would also be available, at the
same level of detail, on all other species. The SBRM, however, is
specifically crafted around the species managed under a subject FMP,
and it is these species, with the addition of threatened and endangered
sea turtles, that drive the allocation of observers across the subject
fishing modes. Contrary to the claim of the commenters, the Councils
explicitly considered expanding this aspect of the SBRM calculations to
include all non-managed species. This is described in section 6.8.1 of
the amendment document and includes the Councils' rationale for not so
expanding the SBRM.
NMFS rejects the claim by the commenters that the agency ``locked''
the public and Councils out of the decision-making process to develop
the SBRM Amendment. The process to development the amendment included
numerous and varied opportunities for the public and the Councils to
fully engage and provide valued input, fulfilling the letter and spirit
of NEPA. The commenters correctly pointed out that the primary analyses
and technical materials were developed by a Fishery Management Action
Team (FMAT) that was chaired by a NMFS staff member, but claim that
this represents a ``flawed'' approach. The choice of a NMFS staff
member to serve as chair of this technical group was suggested by the
Councils as a way to help with staffing resource concerns shared by the
Councils. However, in all respects other than the position of the
group's chair, the membership of the FMAT reflected the standard
operating procedures for Plan Development Teams (PDTs), as used by the
New England Council, as well as FMATs as used by the Mid-Atlantic
Council. The SBRM FMAT included staff from both Councils, the Northeast
Fisheries Science Center, NOAA General Counsel, and the Northeast
Regional Office, all with the requisite expertise and background in the
subject matter.
All activities, analyses, and recommendations of the FMAT were
reported to a Joint Oversight Committee composed of voting member of
both Councils, and all such meetings of the SBRM Committee were held in
public fora with advance notice to the public. Throughout the
development of the amendment, the SBRM Committee held six public
meetings ranging in location from Virginia Beach, VA, to Peabody, MA.
All decisions of the Councils with regards to establishing the range of
alternatives to be considered in the
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amendment, selecting the preferred alternatives, approval of the draft
amendment for release to the public, reviewing the results of the
analyses and information provided by the FMAT, assessing the comments
submitted by the public on the draft amendment and the changes proposed
to address those comments were first vetted through the SBRM Committee
in public meetings. In addition to the six meetings of the SBRM
Committee, the Councils met publicly a total of 13 times to receive
reports on the progress of the SBRM Amendment, to review the decisions
and recommendations of the SBRM Committee, and to formally approve and
adopt the amendment for release to the public and, later, to submit for
Secretarial review. There was also a public meeting at which members of
both Councils' SSCs conducted a formal peer-review of the technical
components of the SBRM Amendment, and two public hearings were held to
provide ample opportunity for interested members of the public to
provide comments on the draft amendment.
Lastly, NMFS disagrees with the assertion by the commenters that
the SBRM Amendment violates NEPA because an EIS was not prepared.
Consistent with NEPA, Council for Environmental Quality (CEQ)
regulations, and NOAA administrative policy, NMFS and the Councils
collaborated to prepare an EA to evaluate the significance of the
environmental impacts expected as a result of the actions considered in
the SBRM Amendment. The results of this assessment are provided in
section 8.9.2 of the amendment, which supports the finding of no
significant impacts (FONSI) signed by the agency on October 16, 2007.
The commenters provided no evidence, nor even any claims, that the
conclusions in the FONSI are not supported by the facts presented in
the EA for this finding. Contrary to the claim of the commenters, NMFS
asserts that the EA considers a sufficient range of alternatives to
satisfy the requirements of NEPA. As described throughout the amendment
(the Executive Summary and chapters 6, 7, and 8), the alternatives
considered by the Councils were structured around seven specific
elements that together comprise the Northeast Region SBRM. Multiple
alternatives were developed and considered for each element and, in
some cases, various sub-options were also developed and considered. As
noted in Appendix E of the amendment, in response to a similar comment
received on the draft amendment, the available permutations of the
various alternatives considered in this action exceeds 1,400 if the
sub-options are not counted. Accounting for the sub-options, the number
of possible outcomes exceeds 2,100 distinct sets of management
alternatives. In addition to the sets of alternatives expressly
analyzed in the EA, the Councils considered, but ultimately rejected
from detailed analysis, an additional four distinct alternatives. These
additional alternatives are described in section 6.8 of the amendment,
and, contrary to the claim of the commenters, include alternatives that
specifically addresses setting alternate CV levels and different
intervals for the SBRM reports.
NMFS disagrees with the commenters that the EA fails to adequately
discuss the purpose, need, and scope of the amendment. All of these
elements are specifically identified and are fully described in chapter
1 of the amendment. The commenters assert that the EA fails to consider
cumulative environmental impacts. NMFS rejects this claim, as section
7.3 of the amendment explicitly provides a discussion of the expected
cumulative effects associated with the action. NMFS asserts that this
treatment of cumulative effects is consistent with CEQ regulations and
current NOAA policy. Regarding protected resources, several elements of
sections 7.1 and 7.2 of the amendment address the potential impacts of
the actions on protected resources, and NMFS considers this treatment,
along with sections 8.3 and 8.8 of the amendment, to be adequate under
all applicable law. Endangered sea turtles are explicitly addressed in
the SBRM (see chapters 5 and 6), and are afforded a priority superior
to all other fish species by ``trumping'' the second and third level
importance filters (i.e., if the results of the second and third level
importance filters would result in an observer allocation to a fishing
mode that is less than the number of sea days calculated to adequately
observe sea turtles, then the higher sea turtle allocation is applied).
As noted throughout the amendment document, the Magnuson-Stevens Act
specifically excludes marine mammals and birds from the definitions of
fish and bycatch and, therefore, the SBRM (because it exists solely as
a Magnuson-Stevens Act construct) need not expressly account for marine
mammals or birds. Therefore, NMFS considers the SBRM Amendment to
adequately address protected resources.
Comment 7: A comment letter written on behalf of four conservation
organizations raised many of the same concerns as the conservation
organization noted above. In particular, the commenters frequently
referred to the results of the technical review described below. The
responses to the comments identified in the technical review are
addressed separately under comment 10. All other points raised in the
comment letter are addressed in this response.
The commenters claim that the SBRM Amendment fails to achieve the
purpose of the action or meet the related requirements of the Magnuson-
Stevens Act and the prior Court orders because it fails to explain the
methods and processes by which bycatch is currently monitored, fails to
determine whether these methods and process should be modified and/or
supplemented, and fails to document the SBRM established for all
Northeast Region FMP fisheries. The commenters claim that the SBRM
Amendment does not explain the methods by which data and information on
discards are obtained by observers. The commenters reiterated the claim
made in comment 4 that the SBRM Amendment ``conclude[s] that observer
coverage is not warranted'' in the mid-water trawl fishery.
The commenters claim that the SBRM Amendment fails to specify
levels of observer coverage required for each FMP, citing concern that
the ``mere performance targets'' leave the actual level of observer
coverage entirely up to the agency. The commenters also claim that the
SBRM fails to adequately cover ``non-managed'' bycatch species.
The commenters claim that NMFS ``prevented'' the New England and
Mid-Atlantic Councils and the public from meaningfully participating in
the development of the SBRM Amendment. Similar to the previous
commenter, the commenters claim that an EIS should have been prepared,
rather than the EA, and that the document therefore does not comply
with NEPA. In particular, the commenters claim that the lack of an EIS:
Limited the opportunities for public participation and stymied the
involvement of the Councils; failed to consider a range of
alternatives; and failed to ensure that decision-makers and the public
are well informed about the potential environmental impacts of the
action. The commenters suggested that the amendment should have been
presented in a more accessible format, claiming that the SBRM is a
``nearly incoherent document.'' The commenters claim that the FMAT
formed to prepare the technical materials for the Councils was a
``failure'' and failed to engage the Councils. The commenters further
claim that the SBRM Amendment was ``carefully steered around the
avoidance
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of the public participation requirements of NEPA,'' and that
opportunities for public participation, including the two public
hearings, were limited to Council meetings with short agenda items and
``little or no'' opportunity for public comment. The commenters also
criticized the amount of time available to review and comment on the
amendment, claiming that much of the document was not available ``in
any form'' until shortly before the Councils approved the document in
June 2007. The commenters concluded by criticizing the 60-day comment
period on the amendment, claiming that this amount of time was
insufficient.
The commenters suggested that NMFS engage independent and objective
scientific expertise, along with the public, and prepare an EIS in
support of a ``significantly revised'' SBRM Amendment. The commenters
claim that the SBRM was never peer reviewed by independent reviewers at
any stage of its development. The commenters recognized that the
document was reviewed by members of the Councils' SSCs, but claim that
these reviewers ``lacked the highly specialized expertise necessary to
conduct a review of this nature,'' and that the reviewers cannot be
considered as independent and objective because they serve as members
of the Councils' SSCs.
Response: NMFS disagrees that the amendment fails to explain the
methods and processes by which bycatch is currently monitored or that
the amendment fails to evaluate whether these methods should be
modified and/or supplemented, noting that chapter 4 addresses these
specific issues. Additional information about the current bycatch data
collection programs is provided in chapter 5 of the amendment and in
associated reference documents that are clearly identified throughout
the amendment. As noted above in response to comments on this issue, it
is incorrect to conclude that the SBRM Amendment in any way suggests
that observer coverage ``is not warranted'' in any fishing mode,
including the New England mid-water trawl mode, which the amendment
indicates would be allocated 316 observer sea days based on the 2004
observer data, a two-fold increase over the actual coverage in this
fishing mode in 2004.
NMFS disagrees with the commenters' implication that the SBRM
Amendment was intended to specify levels of observer coverage required
for each FMP. Nothing in the Magnuson-Stevens Act, or in either
relevant Court order described above, requires that an SBRM include
specific observer coverage levels to be identified for each FMP.
Rather, the intent of the Magnuson-Stevens Act SBRM provision,
supported by the Court, was to establish procedures to determine the
appropriate levels of coverage [See, Oceana II at p. 233 (footnote 38),
where the Court states that ``Oceana I did not require that an FMP
mandate a specific level of observer coverage'']. The amendment clearly
establishes the procedures to be used to make these determinations and
requires that the agency utilize these procedures (``Each year, the
Regional Administrator and the Science and Research Director shall
allocate sufficient at-sea observer coverage to the applicable
fisheries of the Northeast Region in order to achieve a level of
precision . . . no greater than 30 percent for each applicable species
and/or spe