2010 Annual Determination for Sea Turtle Observer Requirements, 27649-27658 [2010-11856]
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BILLING CODE 6560–50–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
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50 CFR Part 222
[Docket No. 0906181067–0167–02]
RIN 0648–XP96
2010 Annual Determination for Sea
Turtle Observer Requirements
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
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*
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
[FR Doc. 2010–11683 Filed 5–17–10; 8:45 am]
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SUMMARY: The National Marine
Fisheries Service (NMFS) publishes its
final Annual Determination (AD) for
2010, pursuant to its authority under the
Endangered Species Act (ESA). Through
this AD, NMFS identifies commercial
fisheries operating in state and Federal
waters in the Atlantic Ocean, Gulf of
Mexico, and Pacific Ocean that will be
required to take observers upon NMFS’
request. The purpose of observing
identified fisheries is to learn more
about sea turtle interactions in a given
fishery, evaluate existing measures to
reduce or prevent prohibited sea turtle
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takes, and to determine whether
additional measures to implement the
prohibition against sea turtle takes may
be necessary. Fisheries identified
through this process will remain on the
AD, and therefore required to carry
observers upon NMFS’ request, for 5
years.
DATES:
Effective June 17, 2010.
ADDRESSES: See SUPPLEMENTARY
INFORMATION for a listing of all Regional
Offices.
FOR FURTHER INFORMATION CONTACT:
Kristy Long, Office of Protected
Resources, 301–713–2322; Ellen Keane,
Northeast Region, 978–282–8476;
Dennis Klemm, Southeast Region, 727–
824–5312; Elizabeth Petras, Southwest
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Region, 562–980–3238; Kim Maison,
Pacific Islands Region, 808–944–2257.
Individuals who use a
telecommunications device for the
hearing impaired may call the Federal
Information Relay Service at 1–800–
877–8339 between 8 a.m. and 4 p.m.
Eastern time, Monday through Friday,
excluding Federal holidays.
SUPPLEMENTARY INFORMATION:
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Availability of Published Materials
Information regarding the Marine
Mammal Protection Act (MMPA) List of
Fisheries (LOF) may be obtained at
https://www.nmfs.noaa.gov/pr/
interactions/lof/ and information
regarding Marine Mammal Stock
Assessment Reports may be obtained at
https://www.nmfs.noaa.gov/pr/sars/ or
from any NMFS Regional Office at the
addresses listed below:
NMFS, Northeast Region, 55 Great
Republic Drive, Gloucester, MA 01930–
2298;
NMFS, Southeast Region, 263 13th
Avenue South, St. Petersburg, FL 33701;
NMFS, Southwest Region, 501 W.
Ocean Blvd., Suite 4200, Long Beach,
CA 90802–4213; or
NMFS, Pacific Islands Region,
Protected Resources, 1601 Kapiolani
Boulevard, Suite 1100, Honolulu, HI
96814–4700.
Purpose of the Sea Turtle Observer
Requirement
Under the ESA, 16 U.S.C. 1531 et seq.,
NMFS has the responsibility to
implement programs to conserve marine
life listed as endangered or threatened.
All sea turtles found in U.S. waters are
listed as either endangered or
threatened under the ESA. Kemp’s
ridley (Lepidochelys kempii),
leatherback (Dermochelys coriacea), and
hawksbill (Eretmochelys imbricata) sea
turtles are listed as endangered.
Loggerhead (Caretta caretta), green
(Chelonia mydas), and olive ridley
(Lepidochelys olivacea) sea turtles are
listed as threatened, except for breeding
colony populations of green turtles in
Florida and on the Pacific coast of
Mexico and breeding colony
populations of olive ridleys on the
Pacific coast of Mexico, which are listed
as endangered. Due to the inability to
distinguish between populations of
green and olive ridley turtles away from
the nesting beach, NMFS considers
these turtles endangered wherever they
occur in U.S. waters. While some sea
turtle populations have shown signs of
recovery, many populations continue to
decline.
Incidental take, or bycatch, in fishing
gear is one of the main sources of sea
turtle injury and mortality nationwide.
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Section 9 of the ESA prohibits the take
(including harassing, harming,
pursuing, hunting, shooting, wounding,
killing, trapping, capturing, or collecting
or attempting to engage in any such
conduct), including incidental take, of
endangered sea turtles. Pursuant to
section 4(d) of the ESA, NMFS has
issued regulations extending the
prohibition of take, with exceptions, to
threatened sea turtles (50 CFR 223.205
and 223.206). Sections 9 and 11 of the
ESA authorize the issuance of
regulations to enforce the take
prohibitions. NMFS may grant
exceptions to the take prohibitions with
an incidental take statement or an
incidental take permit issued pursuant
to ESA section 7 or 10, respectively. To
do so, NMFS must determine that the
activity that will result in incidental
take is not likely to jeopardize the
continued existence of the affected
listed species. In some cases, NMFS has
been able to make this determination
because the fishery is conducted with
modified gear or modified fishing
practices that NMFS has been able to
evaluate. However, for some Federal
fisheries and most state fisheries, NMFS
has not granted an exception primarily
because we lack information about
fishery-turtle interactions. Therefore,
any incidental take of sea turtles in
those fisheries is unlawful as it has not
been exempted from the ESA
prohibition on take.
The most effective way for NMFS to
learn more about sea turtle-fishery
interactions in order to prevent or
minimize take is to place observers
aboard fishing vessels. In 2007, NMFS
issued a regulation (50 CFR 222.402) to
establish procedures through which
each year NMFS will identify, pursuant
to specified criteria and after notice and
opportunity for comment, those
fisheries in which the agency intends to
place observers (72 FR 43176, August 3,
2007). These regulations specify that
NMFS may place observers on U.S.
fishing vessels, either recreational or
commercial, operating in U.S. territorial
waters, the U.S. exclusive economic
zone (EEZ), or on the high seas, or on
vessels that are otherwise subject to the
jurisdiction of the U.S. Failure to
comply with the requirements under
this rule may result in civil or criminal
penalties under the ESA.
NMFS and/or interested cooperating
entities will pay the direct costs for
vessels to carry observers. These include
observer salary and insurance costs.
NMFS may also evaluate other potential
direct costs, should they arise. Once
selected, a fishery will be eligible to be
observed for five years without further
action by NMFS. This will enable NMFS
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to develop an appropriate sampling
protocol to investigate whether, how,
when, where, and under what
conditions incidental takes are
occurring; to evaluate whether existing
measures are minimizing or preventing
takes; and to determine whether
additional measures are needed to
implement ESA take prohibitions and
conserve turtles.
Process for Developing an Annual
Determination
Pursuant to 50 CFR 222.402, the
Assistant Administrator for Fisheries,
NOAA (AA), in consultation with
Regional Administrators and Fisheries
Science Center Directors, develops a
proposed annual determination
identifying which fisheries are required
to carry observers, if requested, to
monitor potential interactions with sea
turtles. NMFS provides an opportunity
for public comment on any proposed
determination. The determination is
based on the best available scientific,
commercial, or other information
regarding sea turtle-fishery interactions;
sea turtle distribution; sea turtle
strandings; fishing techniques, gears
used, target species, seasons and areas
fished; or qualitative data from logbooks
or fisher reports. Specifically, this
determination is based on the extent to
which:
(1) The fishery operates in the same
waters and at the same time as sea
turtles are present;
(2) The fishery operates at the same
time or prior to elevated sea turtle
strandings; or
(3) The fishery uses a gear or
technique that is known or likely to
result in incidental take of sea turtles
based on documented or reported takes
in the same or similar fisheries; and
(4) NMFS intends to monitor the
fishery and anticipates that it will have
the funds to do so.
The AA used the most recent version
of the annually published MMPA List of
Fisheries (LOF) as the comprehensive
list of commercial fisheries for
consideration. The LOF includes all
known state and Federal commercial
fisheries that occur in U.S. waters. The
classification scheme used for fisheries
on the LOF would not be relevant to this
process. Unlike the LOF process, an
annual determination may also include
recreational fisheries likely to interact
with sea turtles on the basis of the best
available information.
NMFS consulted with appropriate
state and Federal fisheries officials and
other entities to identify which
fisheries, both commercial and
recreational, should be considered in
the annual determination. Although the
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comments and recommendations
provided to NMFS by states were based
upon the best available information on
their fisheries, NMFS received more
recommendations for fisheries to
include on the 2010 AD than is feasible
at this time based on the four previously
noted criteria (50 CFR 222.402(a)).
The AD is not an exhaustive or
comprehensive list of all fisheries with
documented or suspected takes of sea
turtles; there are additional fisheries
that NMFS remains concerned about.
For these additional fisheries, NMFS
may already be addressing incidental
take through another mechanism (e.g.,
rulemaking to implement modifications
to fishing gear and/or practices) or will
consider adding them to future annual
determinations based on the four
previously noted criteria (50 CFR
222.402(a)).
Notice of a final determination, such
as the 2010 AD, will be published in the
Federal Register and made in writing to
individuals permitted for each fishery
identified for monitoring. NMFS will
also notify state agencies and provide
notification through publication in local
newspapers, radio broadcasts, and other
means, as appropriate. Once included in
a final determination, a fishery will
remain eligible for observer coverage for
five years to enable the design of an
appropriate sampling program and to
ensure collection of sufficient scientific
data for analysis. If NMFS determines
that more than five years are needed to
obtain sufficient scientific data, NMFS
will include the fishery in the proposed
AD again prior to the end of the fifth
year. As part of the 2010 AD, NMFS
included, to the extent practicable,
information on the fisheries or gear
types to be sampled, geographic and
seasonal scope of coverage, and any
other relevant information. After
publication of a final AD, a 30–day
delay in effective date for implementing
observer coverage will follow, except for
those fisheries where the AA has
determined that there is good cause
pursuant to the Administrative
Procedure Act to make the rule effective
without a 30–day delay.
Implementing Observer Coverage in a
Fishery Listed on the 2010 Annual
Determination
The design of any observer program
for fisheries identified through the AD
process, including how observers will
be allocated to individual vessels,
would vary among fisheries, fishing
sectors, gear types, and geographic
regions and would ultimately be
determined by the individual NMFS
Regional Office, Science Center, and/or
observer program. During the program
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design, NMFS will be guided by the
following standards for distributing and
placing observers among fisheries
identified in the AD and vessels in those
particular fisheries:
(1) The requirements to obtain the
best available scientific information;
(2) The requirement that observers be
assigned fairly and equitably among
fisheries and among vessels in a fishery;
(3) The requirement that no
individual person or vessel, or group of
persons or vessels, be subject to
inappropriate, excessive observer
coverage; and
(4) The need to minimize costs and
avoid duplication, where practicable.
Vessels subject to observer coverage
under this rule must comply with
observer safety requirements specified
at 50 CFR 600.725 and 50 CFR 600.746.
Specifically, 50 CFR 600.746(c) requires
vessels to provide adequate and safe
conditions for carrying an observer and
conditions that allow for operation of
normal observer functions. To provide
such conditions, a vessel must comply
with the applicable regulations
regarding observer accommodations (see
50 CFR parts 229, 300, 600, 622, 635,
648, 660, and 679) and possess a current
USCG Commercial Fishing Vessel Safety
Examination decal or a USCG certificate
of examination. A vessel that fails to
meet these requirements at the time an
observer is to be deployed on the vessel
is prohibited from fishing, 50 CFR
600.746(f), unless NMFS determines
that an alternative platform (e.g., a
second vessel) may be used. In any case,
all fishermen on a vessel must cooperate
in the operation of observer functions.
Observer programs designed or carried
out in accordance with 50 CFR 222.404
would be required to be consistent with
existing observer-related NOAA policies
and regulations, such as those under the
Fair Labor and Standards Act (29 U.S.C.
201 et seq.), the Service Contract Act (41
U.S.C. 351 et seq.), Observer Health and
Safety regulations (50 CFR 600), and
other relevant policies.
Fisheries not included on the 2010
AD may still be observed under a
different authority than the ESA (e.g.,
MMPA, MSA).
Additional information on observer
programs in commercial fisheries can be
found on the NMFS National Observer
Program’s website: https://
www.st.nmfs.gov/st4/nop/; links to
individual regional observer programs
may also be found on this website.
Comments and Responses
NMFS received comments from 3
individual members of the public,
Environmental Defense Fund, Oceana,
Garden State Seafood Association, Cape
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Seafoods, Inc., Lund’s Fisheries, Inc.,
Northern Pelagic Group LLC, Western
Sea Fishing Company, Mid-Atlantic
Fishery Management Council, and the
States of Connecticut, Maryland, and
New Jersey on the proposed 2010 AD
(74 FR 59508, November 18, 2009).
Comments on issues outside the scope
of the AD were noted, but are not
responded to in this final rule.
General Comments
Comment 1: Several commenters
support including 19 fisheries on the
2010 AD.
Response: NMFS agrees and includes
19 fisheries on the 2010 AD.
Comment 2: The State of New Jersey
inquired whether the fisheries to be
observed listed in Table 1 are in priority
order.
Response: Table 1 is somewhat
prioritized by gear type (trawl, gillnet,
trap/pot, and pound net/weir/seine);
specific fisheries within those gear types
are alphabetized. The order of those gear
types represents NMFS’ current
priorities under the NMFS’ Strategy for
Sea Turtle Conservation and Recovery
in Relation to Atlantic Ocean and Gulf
of Mexico Fisheries (‘‘Strategy’’).
Fisheries operating in the Pacific Ocean
will be considered similarly. However,
NMFS’ Regional Observer Programs are
implemented somewhat independently
based on several factors including
available funding, staff resources, the
number of certified observers in a given
region, etc. Therefore, NMFS will
consider all of these factors when
deciding which fisheries to observe in a
given year. For example, increasing
coverage within existing observer
programs may be more feasible than
beginning a new program in a given year
based on available funding and staff
resources in a particular region.
Comment 3: Cape Seafoods, Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association inquired how and when
fisheries are removed from the AD. The
commenters suggest that there be a
process outlined in this final rule for
removing fisheries before the 5 years
expire.
Response: The amount of time that
fisheries remain on the AD was the
subject of the previous rulemaking that
implemented the observer requirement
(72 FR 43176, August 3, 2007); this
rulemaking does not amend those
regulations or implement new
regulations. The regulations at 50 CFR
222.403(a) specify that once selected, a
fishery remains eligible for observer
coverage for five years.
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Comment 4: Cape Seafoods, Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association suggest adding a criterion
for including fisheries on the AD that
considers past observer coverage.
Response: The criteria that NMFS
considers when proposing to include a
fishery on the AD were the subject of
the previous rulemaking that
implemented the observer requirement
(72 FR 43176, August 3, 2007); this
rulemaking does not amend those
regulations or implement new
regulations.
Comment 5: The State of Connecticut
notes that the report from the 2008
Observer Workshop includes a
statement about using state observers
under NMFS’ authority to implement
this observer requirement and they
would like to have state observers
certified for this purpose.
Response: Since the workshop in
2008, NMFS has determined that the
regulations in 50 CFR 222.402 provide
authorization only for Federal observer
programs implemented by NMFS. The
State may be able to act as the Observer
Service Provider and enter into an
agreement with NMFS contingent upon
certification of those observers by NMFS
(i.e., those state observers are NMFScertified).
Comment 6: Cape Seafoods, Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association suggests that broad gear
categories do not pose similar risks to
sea turtles and recommends that
fisheries be examined on a case-by-case
basis for temporal/spatial overlap with
turtle distribution, while accounting for
regional fishing practices and past/
current observer coverage.
Response: The universe of
commercial fisheries considered for the
Annual Determination is based on the
MMPA LOF. If the LOF defines a fishery
based on broad gear type, NMFS must
also use that same fishery on the Annual
Determination. If the commenters have
suggestions for re-defining fisheries on
the MMPA LOF, they should consider
commenting during the 2011 LOF
process. See Comments on Observer
Programs below for additional
information on how past observer
coverage is factored into sampling
designs.
Comment 7: Cape Seafoods, Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association inquired how this observer
requirement would yield statistically
rigorous information when statistically
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valid information or accurate data on
the status and trends of sea turtles has
not been provided.
Response: This comment appears to
be directed at the rule promulgated by
NMFS on August 3, 2007, codified at 50
CFR Part 222 Subpart D, and is thus
outside the scope of this rulemaking.
However, NMFS responds to clarify
that, as stated in the preamble to that
rulemaking: ‘‘Sampling designs for all
NMFS observer programs are developed
to provide statistically valid information
and to produce results that will
contribute to the body of best available
science. The sampling design will vary
depending on many factors, including
the fishery to be observed, the spatial
and temporal variability in the fishery
and species observed, and the overall
goals of the observer program. Once a
fishery is selected for observer coverage,
a sampling design will be developed to
yield statistically valid results.’’ [72 FR
43176, August 3, 2007]
Regardless of the data available on the
status and trends of sea turtles, this
program will collect statistically valid
information on sea turtle takes. NMFS
continues to work to better understand
the status and trends of sea turtle
populations, including through survey
efforts, population modeling, and status
reviews.
Comment 8: Cape Seafoods, Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association further inquired how
bycatch rates and estimates would be
applied during ESA section 7 and 10
consultations as well as broad-based
gear regulations.
Response: This comment is beyond
the scope of this rulemaking. The
preamble to the rule codified at 50 CFR
Part 222 Subpart D describes how the
information gathered will be used (72
FR 43176, August 3, 2007). Because data
have not yet been collected nor
analyzed, NMFS can not now identify
what, if any, management actions it
might take in response to those data.
Comments on Observer Programs
Comment 9: Environmental Defense
Fund recommends using new
technologies, including video
monitoring to eliminate observer bias,
increase level of monitoring (as it
becomes more cost effective) and
monitor unobservable vessels.
Response: New technologies for
monitoring fisheries (commonly referred
to as ‘‘electronic monitoring’’ or EM)
offer many benefits of interest to NMFS.
However, their efficacy in meeting
monitoring objectives varies by fishery
and monitoring goal. EM studies,
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including video monitoring, are ongoing
in many NMFS regions, and the results
are promising. The ability of these
technologies to meet monitoring
objectives has primarily been evaluated
in experimental situations; many
questions still remain as to their efficacy
and true cost. NMFS generally supports
the use of EM to augment at-sea
observer coverage, and fully supports
the use of EM, as well as other
alternative monitoring methods, to
cover unobservable vessels. NMFS will
continue to work through its
cooperative research and fisheries
observer programs to evaluate how EM
technology may be used to supplement
observer programs, including those
implemented under the AD.
Comment 10: The State of New Jersey
requested training in observer protocols
for state personnel to augment NMFS
coverage in state waters under State
authority and increase effectiveness.
Response: The Northeast Fisheries
Observer Program (NEFOP) has helped
individual states develop their own
state fisheries observer programs, and
will continue to do so as long as the
demand doesn’t compromise the
training needs of NEFOP. The support
NEFOP provides includes training, logs,
manuals, protocols and entry screens.
Comment 11: The State of New Jersey
inquired how observer coverage will be
allocated across fisheries and requested
that the State be consulted each year
during the vessel selection process.
Response: Observer coverage is
allocated in proportion to fishing effort
by time/area. All active vessels,
indentified for observer coverage within
a particular time/area, may be randomly
selected. Current NEFOP protocols
prohibit repeat trips on the same vessel,
during a 30 day period, if other vessels
are active and have not been selected.
NEFOP attempts to ensure that observer
coverage is fair and equitable, without
overburdening a particular fisherman or
fishery. NEFOP posts the sea day
schedule on the following website:
https://www.nefsc.noaa.gov/femad/fsb.
This website provides the chance for all
interested parties to review the planned
coverage. NEFOP would welcome the
opportunity to work with individual
states when developing a list of vessels
to be selected for that proposed
coverage.
Comment 12: Cape Seafoods, Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association inquired how NMFS will
implement the requirements in a way
that no fisherman or group of fishermen
will be expected to carry excessive
observer coverage. Further, Garden State
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Seafood Association believes that NJ
fishermen have been overburdened with
an excessive share of observer training
trips/coverage (e.g., 72 trips in 2005).
Response: As previously described,
NEFOP makes every legitimate attempt
to not overburden a particular fisherman
or fishery. Days are allocated in
proportion to fishing effort by time/area.
From 2000 to 2005, the NEFOP grew
from 1,200 sea days per year to 12,000
sea days per year; increasing from 12 to
120 observers. That increase
necessitated additional training trips.
Training trips require that an
experienced observer shadow a new
observer until they are fully certified in
all sampling protocols. Gillnet sampling
protocols, per NEFSC scientists
conducting harbor porpoise bycatch
analysis, require observers to observe
the net for harbor porpoise ‘‘fall outs’’
during retrieval, instead of sampling
discarded fish. These trips are referred
to as ‘‘limited’’ gillnet trips because of
the limited sampling of fish. All of the
gillnet days on the NEFOP sea day
schedule for protected species are
‘‘limited’’ days. This includes both New
England and mid-Atlantic areas. In
addition to these ‘‘limited’’ gillnet days,
scientists conducting fish stock
assessments also populated the sea day
schedule with gillnet days, but unlike
the ‘‘limited’’ days, complete sampling
of all discards was required. The
majority of these ‘‘complete’’ days were
assigned to areas in New Jersey and
north. Prior to December 2005, in order
to provide the best training trips
possible, new observers from southern
ports were often sent to New Jersey, or
ports farther north, for those important
training trips. This resulted in
proportionally more training trips
occurring in New Jersey. Once this
problem was brought to the attention of
NEFOP, protocols were changed so that
new observers, during their training
trips, could use ‘‘complete’’ sampling
protocols regardless of the port used for
training. This change was made in
December 2005, and since then NEFOP
has not received any reports that this
issue continues to be a problem.
Comment 13: Cape Seafoods, Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association expressed concern about
the competing needs (e.g., population
dynamics, food habits, protected
species, fisheries management, etc.) for
a given observer program and how
NMFS intends to balance those needs
with observer program design/
implementation. The commenters also
note that the proposed 2010 AD
indicates that the program design could
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be the responsibility of a regional office,
science center, or observer program. The
commenters suggest that clear lines of
responsibility should be placed on
program design/implementation.
Response: Within each of the six
NMFS Regional Observer Programs, the
responsibility for observer program
design and implementation is clearly
defined. Manual and protocol revisions
occur regularly based on the changing
needs of end users (e.g., NMFS
managers). For example, NEFOP works
closely with all end users to ensure that
the data collected by observers is
relevant and meets their needs. Those
needs, for example, could include
compliance monitoring, data collection
for regulatory development, or data
collection for stock assessments. To
date, NEFOP has been able to
successfully balance the needs of all end
users.
Comment 14: Cape Seafoods, Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association suggested that NMFS
consider social and economic burdens
of sea turtle observer coverage with
respect to total observer coverage.
Response: See Response to Comment
11 and the Classification section below.
Comment 15: One commenter
inquired whether minimum standards
for selecting a vessel, in each of the
fisheries, to carry an observer have been
identified. The commenter notes
potential for introducing bias and
suggests NMFS Observer Programs
develop methods for reducing the
number of unobservable vessels.
Response: With the exception of
certain safety requirements (e.g.,
possessing a current U.S. Coast Guard
commercial fishing vessel safety decal),
minimum national standards for vessel
selection do not exist. Regional observer
programs perform routine analyses to
diagnose and correct for bias in vessel
selection. A 2006 NMFS workshop
(report available from: https://
www.st.nmfs.noaa.gov/st4/nop/
workshops.html) reviewed vessel
selection procedures and documented
analytical methods and tools that could
be used to assess the occurrence and
magnitude of bias. Workshop
participants identified alternative
selection methods that could reduce or
eliminate sources of bias, such as using
alternative platforms or electronic
monitoring to address unobservable
vessels.
Comments on Trawl Fisheries
Comment 16: The Mid-Atlantic
Fishery Management Council suggested
removing Illex from the list of species
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targeted with flynets because while they
are included in the mid-Atlantic bottom
trawl general category, the Illex fishery
is not prosecuted using flynets.
Response: The flynet fishery
description in the proposed 2010 AD is
based on the fishery as defined under
the Marine Mammal Protection Act
(LOF). NMFS will consider revising the
characterization of the flynet fishery in
a future LOF.
Comment 17: Cape Seafoods Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association recommend removing the
mid-Atlantic mid-water trawl (including
pair trawl) for mackerel from the 2010
AD as optimum mackerel trawl fishing
occurs in areas where the sea surface
temperature is less than 7 degrees
Celsius. The commenters note that this
temperature regime is not in the range
one would expect sea turtles to
normally thrive.
Response: Sea turtles are
poikilotherms whose internal body
temperature is affected by the ambient
environment. They undertake routine
migrations along the coast limited by
seasonal water temperatures.
Loggerheads have been observed in
waters with surface temperatures of 7°
to 30° C, but water temperatures ≥11° C
are most favorable (Shoop and Kenney
1992; Epperly et al., 1995). During the
CETAP aerial survey of the outer
continental shelf from Cape Hatteras,
North Carolina, to Cape Sable, Nova
Scotia, leatherbacks were sighted in
waters within a sea surface temperature
range similar to that observed for
loggerheads; from 7°–27.2° C. However,
leatherbacks appear to have a greater
tolerance for colder waters in
comparison to loggerhead sea turtles
since more leatherbacks were found at
lower temperatures (Shoop and Kenney
1992).
As defined on the LOF, the mid-water
trawl fishery for Atlantic mackerel is
one component of the overall midAtlantic mid-water trawl (including pair
trawl) fishery. This fishery targets
Atlantic mackerel, chub mackerel, and
other miscellaneous pelagic species
(e.g., Atlantic herring). The component
of the fishery targeting mackerel uses
the same gear type and fishing practices
as the rest of the fishery targeting other
species. Therefore, NMFS is including
this fishery on the 2010 AD to more
adequately observe this gear type in
areas and during times where it overlaps
with sea turtle distribution.
Comments on Gillnet Fisheries
Comment 18: The State of
Connecticut provided information on
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the Long Island Sound commercial
gillnet fishery operating in CT waters.
The State noted that there have been
less than 19 active fixed gillnetters
operating during the months of May
through October, no interactions with
sea turtles have been documented, and
there were a limited number of sea
turtle strandings in CT waters (n=12)
from 1998 to 2004. The commenter
states that it is unlikely that there are
enough turtles present in CT waters and
likely to be at risk to justify observer
coverage in this fishery. The commenter
also suggests that monitoring this
fishery would not contribute to
meaningful information on sea turtle
bycatch.
Response: The portion of the Long
Island Sound inshore gillnet fishery
operating in CT waters is one
component of the Long Island Sound
inshore gillnet fishery as defined on the
LOF. The fishery includes all gillnet
fisheries setting nets west of a line from
the north fork of the eastern end of Long
Island, NY (Orient Point to Plum Island
to Fisheries Island) to Watch Hill, RI (59
FR 43703, August 25, 1994). Northeast
waters are an important developmental
habitat for hard-shelled sea turtles and
sea turtles occur in Long Island Sound.
As described in the proposed rule, sea
turtles are vulnerable to entanglement
and drowning in gillnets. Past observer
coverage in this fishery is limited to a
small number of federally observed
trips. Therefore, NMFS is including this
fishery on the 2010 AD to better
understand this fishery and how it may
impact sea turtles. NMFS will consider
information on sea turtle distribution
and the spatial and temporal extent of
gillnet fisheries operating in Long Island
Sound in designing an appropriate
sampling program for this fishery.
Comment 19: Garden State Seafood
Association recommends excluding NJbased vessels that target bluefish and
croaker in the Mid-Atlantic gillnet
fishery because there were 179 trips
observed between 2000 and 2005 and no
sea turtle takes were documented.
Response: Fisheries observers in the
mid-Atlantic have documented take of
loggerhead, green, Kemp’s ridley, and
leatherback turtles in sink gillnet gear
from Cape Cod to North Carolina.
Observed interactions have occurred on
trips targeting a variety of species,
including bluefish and Atlantic croaker.
From 1995–2006, the average annual
bycatch estimate of loggerheads
captured in mid-Atlantic sink gillnet
gear was 350 turtles (Murray 2009).
Bycatch rates were correlated with
latitude, sea surface temperature, and
mesh size. Highest predicted bycatch
rates occurred in warm waters of the
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southern mid-Atlantic, in large-mesh (≤
17.8 cm) gillnet gear (Murray 2009).
Gillnet fisheries, including those
targeting bluefish and croaker, that
overlap with sea turtle distribution have
the potential to take sea turtles.
Typically, observer coverage is
allocated in proportion to fishing effort,
by month and port, with vessels
selected randomly for coverage. Vessels
are selected based on gear type, not
target species. If the majority of the
gillnet vessels fishing out of a particular
port targeted bluefish, the data should
reflect that.
To better understand the interactions
of these fisheries with sea turtles, NMFS
is including the mid-Atlantic gillnet
fishery on the 2010 AD to focus observer
coverage during times and areas where
sea turtles are known to occur.
Information on sea turtle distribution
and the spatial and temporal extent of
these fisheries will be considered in
designing an appropriate sampling
program for the fishery.
Comment 20: Oceana recommended
including all Gulf of Mexico and
Caribbean gillnet fisheries on the 2010
AD because of similarities to other
gillnet fisheries as well as the large
number of participants.
Response: NMFS recognizes that
gillnet fisheries in areas other than those
identified in the first AD may pose
similar issues for sea turtles. However,
the regulations implementing this
observer requirement at 50 CFR 222.402
specifically state that the annual
determination will be based on the
extent to which: (1) The fishery operates
in the same waters and at the same time
as sea turtles are present; (2) The fishery
operates at the same time or prior to
elevated sea turtle strandings; or (3) The
fishery uses a gear or technique that is
known or likely to result in incidental
take of sea turtles based on documented
or reported takes in the same or similar
fisheries; and (4) NMFS intends to
monitor the fishery and anticipates that
it will have the funds to do so. Although
many fisheries meet one or more of the
first three requirements, NMFS must
also consider the fourth criterion, which
is dependent upon available agency
resources. Given the agency’s current
resources for implementing this
program, NMFS is not including any
gillnet fisheries in the Gulf of Mexico or
Caribbean on the 2010 AD. However,
this is an annual process and NMFS will
consider including additional fisheries
on future ADs based upon the
aforementioned criteria.
Comments on Trap/Pot Fisheries
Comment 21: The State of
Connecticut provided information on
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the commercial lobster pot fishery in
Connecticut and a description of the
state monitoring program. Specifically,
since 1982, the CT Department of
Environmental Protection’s Marine
Fisheries Division has observed 13,693
multi-trap trawl hauls on 643
commercial lobster trips in Long Island
Sound. During the program, a single
take of a sea turtle was documented in
August 2009; a leatherback turtle was
observed entangled in a vertical line.
Response: NMFS appreciates
receiving detailed information on the
monitoring program and CT commercial
lobster pot fishery. This fishery is one
component of the overall Northeast/
Mid-Atlantic American Lobster Trap/
Pot fishery, which operates from Maine
to New Jersey and may extend as far
south as Cape Hatteras, NC. As noted by
the commenter and described in the
proposed rule (74 FR 59508, November
18, 2009), sea turtles are known to
become entangled in the end lines (also
called vertical lines) of trap/pot gear.
There have also been anecdotal reports
that sea turtles may interact with the
trap/pot itself. NMFS currently has only
limited data on sea turtle bycatch in this
fishery. NMFS is including this fishery,
focusing on waters south of
Massachusetts where sea turtles more
commonly occur, on the 2010 AD to
obtain information on sea turtle bycatch
and how turtles may interact with the
gear. The information provided will be
considered in designing an appropriate
sampling program for this fishery.
Comments on Longline Fisheries
Comment 22: Oceana recommends
including all longline fisheries, both
pelagic and bottom longlines, on the
2010 AD. Specifically, the commenter
noted the need for additional observer
coverage in the Gulf of Mexico reef fish
bottom longline fishery as well as new
observer programs for the Northeast/
mid-Atlantic bottom longline, Caribbean
snapper grouper and other bottom
longline fisheries.
Response: The purpose of the sea
turtle observer requirement and the AD
is ultimately to implement ESA sections
9 and 4(d), which prohibit the
incidental take of endangered and
threatened sea turtles, respectively.
Another purpose of the AD is to learn
more about sea turtle-fishery
interactions in the identified fisheries in
order to have information necessary to
provide exemptions to the take
prohibitions, consistent with ESA
sections 4(d), 7 and 10, if warranted for
certain fisheries.
NMFS did not include any pelagic
longline fisheries on the 2010 AD
because all commercial pelagic longline
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fisheries as included on the MMPA LOF
are currently observed for sea turtles
and incidental takes authorized.
Similarly, the Gulf of Mexico reef fish
bottom longline fishery is currently
observed for sea turtles and takes
authorized. Therefore, including these
fisheries on the 2010 AD would be
duplicative at this time.
NMFS evaluated the aforementioned
criteria in 50 CFR 222.402 and
determined that the agency could not
satisfy the fourth criterion at this time
with regard to including the other
bottom longline fisheries recommended
by the commenter. However, this is an
annual process and NMFS will consider
including additional fisheries, including
longline fisheries, on future ADs.
hsrobinson on DSK69SOYB1PROD with RULES
Comments on Recreational Fisheries
Comment 23: Cape Seafoods Inc.,
Lund’s Fisheries, Inc., Northern Pelagic
Group LLC, Western Sea Fishing
Company, and Garden State Seafood
Association suggests noting that
recreational fisheries are responsible for
sea turtle deaths and recommends that
NMFS specify a clear process for
including recreational fisheries on the
AD. Specifically, they recommend using
the new recreational fishing registry
implemented in January 2009 to identify
fisheries.
Response: NMFS recognizes that
recreational fisheries may also
incidentally take sea turtles and,
therefore, included recreational fisheries
under the observer requirement at 50
CFR 222.401.
NMFS appreciates the commenter’s
suggestion to use the recreational
fishing registry and will consider
including recreational fisheries on
future ADs.
Comment 24: Oceana recommended
including recreational fisheries on the
2010 AD.
Response: NMFS considered
recreational fisheries in developing the
proposed 2010 AD, but the agency did
not feel we had enough information to
develop an observer program. Further,
NMFS determined that the agency could
not satisfy the criterion at 50 CFR
222.402(a)(4) required to include a
fishery on the AD. As noted in the
response to Comment 23, NMFS will
use the information from the
recreational fishing registry, along with
other information from the Marine
Recreational Information Program, to
obtain the necessary information to
consider including specific recreational
fisheries on a future AD.
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Addition of Fisheries on the 2010
Annual Determination
NMFS is including 19 fisheries (17 in
the Atlantic Ocean and Gulf of Mexico
and 2 in the Pacific Ocean) on the 2010
AD. These 19 fisheries, described below
and listed in Table 1, represent several
gear types, including trawl, gillnet, trap/
pot, and pound net/weir/seine. For a
complete description of the information
and state recommendations NMFS used
in developing the 2010 AD, please see
the proposed rule (74 FR 59508,
November 18, 2009).
Trawl Fisheries
Based on the information provided by
states and the best available scientific
information, NMFS includes the
following trawl fisheries on the 2010
AD.
Atlantic Shellfish Bottom Trawl Fishery
The Atlantic shellfish bottom trawl
fishery (estimated 972 vessels/persons)
encompasses the calico scallop trawl,
crab trawl, Georgia/South Carolina/
Maryland whelk trawl, Gulf of Maine/
Mid-Atlantic sea scallop trawl, and Gulf
of Maine northern shrimp trawl (71 FR
2006, January 4, 2006). This fishery
extends from Maine through Florida.
NMFS is particularly interested in
observing this fishery in waters off of
Massachusetts and south as sea turtles
more commonly occur in this area.
NMFS includes this fishery on the 2010
AD based on documented interactions
with sea turtles in this and other bottom
trawl fisheries and the need to obtain
more information on the interactions in
this fishery.
Mid-Atlantic Bottom Trawl Fishery
Bottom otter trawl nets include a
variety of net types, including flynets,
which are high profile trawls. The ‘‘MidAtlantic bottom trawl fishery’’ as
described in this proposed AD includes
both the mid-Atlantic bottom trawl
fishery and the mid-Atlantic flynet
fishery as defined on the LOF.
The Mid-Atlantic bottom trawl fishery
(estimated <1,000 vessels/persons), as
defined on the LOF, uses bottom trawl
gear to target species including, but not
limited to, bluefish, croaker, monkfish,
summer flounder (fluke), winter
flounder, silver hake (whiting), spiny
dogfish, smooth dogfish, scup, and
black sea bass. The fishery occurs yearround from Cape Cod, MA, to Cape
Hatteras, NC, in waters west of 72° 30’
W. long. and north of a line extending
due east from the North Carolina/South
Carolina border.
The Mid-Atlantic flynet fishery
(estimated 21 vessels/persons), as
defined on the LOF, is a multi-species
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fishery composed of nearshore and
offshore components that operate along
the east coast of the mid-Atlantic United
States. The nearshore fishery operates
from October to April inside of 30
fathoms (180 ft; 55 m) from New Jersey
to North Carolina. This nearshore
fishery targets Atlantic croaker,
weakfish, butterfish, harvestfish,
bluefish, menhaden, striped bass,
kingfish species, and other finfish
species. The offshore component
operates from November to April
outside of 30 fathoms (180 ft; 55 m)
from the Hudson Canyon off New York,
south to Hatteras Canyon off North
Carolina. These deeper water fisheries
target bluefish, Atlantic mackerel, Loligo
squid, black sea bass, and scup (72 FR
7382, February 15, 2007).
NMFS includes this fishery on the
2010 AD to more adequately observe
this gear type where and when it
overlaps with sea turtle distribution.
Mid-Atlantic Mid-water Trawl
(including pair trawl) Fishery
The Mid-Atlantic mid-water trawl
fishery (estimated 620 vessels/persons)
primarily targets Atlantic mackerel,
chub mackerel, and miscellaneous other
pelagic species. NMFS includes this
fishery on the 2010 AD to more
adequately observe this gear type in
areas and during times where it overlaps
with sea turtle distribution.
Southeastern U.S. Atlantic, Gulf of
Mexico Shrimp Trawl Fishery
The Southeastern U.S. Atlantic, Gulf
of Mexico shrimp trawl fishery
(estimated >18,000 vessels/persons)
targets shrimp using various types of
trawls; NMFS would focus on the
component of the fishery that uses
skimmer trawls for the 2010 AD.
Skimmer trawls are used primarily in
inshore/inland shallow waters (typically
less than 20 ft (6.1 m)) to target shrimp.
NMFS is including the Southeastern
U.S. Atlantic, Gulf of Mexico shrimp
trawl fishery, to focus observer coverage
in the component of the fishery that
uses skimmer trawls, on the 2010 AD.
Gillnet Fisheries
CA Halibut, White Seabass and Other
Species Set Gillnet Fishery (>3.5 in
mesh)
The CA halibut, white seabass, and
other species set gillnet fishery
(estimated 58 vessels/persons) targets
halibut, white seabass, and other species
from the U.S.-Mexico border north to
Monterey Bay using 200 fathom (1,200
ft; 366 m) gillnet with a stretch mesh
size of 8.5 in (31.6 cm). NMFS includes
this fishery on the 2010 AD because it
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operates in the same waters that turtles
are known to occur and this gear type
is known to result in the incidental take
of sea turtles based on documented
takes in similar fisheries.
CA Yellowtail, Barracuda, and White
Seabass Drift Gillnet Fishery (mesh size
>3.5 in. and <14 in.)
The CA yellowtail, barracuda, and
white seabass drift gillnet fishery (24
vessels/persons) targets primarily
yellowtail and white seabass, and
secondarily barracuda, with target
species typically determined by market
demand on a short-term basis. NMFS
includes this fishery on the 2010 AD
because it operates in the same waters
that turtles are known to occur and this
gear type is known to result in the
incidental take of sea turtles based on
documented takes in similar fisheries.
Chesapeake Bay Inshore Gillnet Fishery
The Chesapeake Bay inshore gillnet
fishery (estimated 45 vessels/persons)
targets menhaden and croaker using
gillnet gear with mesh sizes ranging
from 2.75–5 in (7–12.7 cm), depending
on the target species. NMFS includes
this fishery on the 2010 AD because sea
turtles are known to occur in the same
areas where the fishery operates, takes
have been previously documented in
similar gear, and the fishery operates
during a period of high sea turtle
strandings.
Long Island Inshore Gillnet Fishery
The Long Island Sound inshore gillnet
fishery (estimated 20 vessels/persons)
includes all gillnet fisheries setting nets
west of a line from the north fork of the
eastern end of Long Island, NY (Orient
Point to Plum Island to Fishers Island)
to Watch Hill, RI (59 FR 43703, August
25, 1994). NMFS includes this fishery in
the 2010 AD because sea turtles are
known to occur in the same areas where
the fishery operates and takes have been
documented in similar gear types.
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Mid-Atlantic Gillnet Fishery
The Mid-Atlantic gillnet fishery
(estimated 7,596 vessels/persons) targets
monkfish, spiny dogfish, smooth
dogfish, bluefish, weakfish, menhaden,
spot, croaker, striped bass, large and
small coastal sharks, Spanish mackerel,
king mackerel, American shad, black
drum, skate spp., yellow perch, white
perch, herring, scup, kingfish, spotted
seatrout, and butterfish. NMFS includes
this fishery on the 2010 AD to focus
observer coverage during times and in
areas where sea turtles are known to
occur.
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Northeast Sink Gillnet Fishery
Atlantic Mixed Species Trap/Pot Fishery
The Northeast sink gillnet fishery
(estimated ≤6,455 vessels/persons)
targets Atlantic cod, haddock, pollock,
yellowtail flounder, winter flounder,
witch flounder, American plaice,
windowpane flounder, spiny dogfish,
monkfish, silver hake, red hake, white
hake, ocean pout, skate spp, mackerel,
redfish, and shad. NMFS includes this
fishery on the 2010 AD to focus observer
coverage during times and in areas
where sea turtles are known to occur,
particularly in waters off Massachusetts
and waters south of this area.
The Atlantic mixed species trap/pot
fishery (unknown number of vessels/
persons) targets species including, but
not limited to, hagfish, shrimp, conch/
whelk, red crab, Jonah crab, rock crab,
black sea bass, scup, tautog, cod,
haddock, pollock, redfish (ocean perch),
white hake, spot, skate, catfish, and
stone crab. This fishery as defined on
the MMPA LOF also includes American
eel as a target species; however, there is
also a Category III American eel trap/pot
fishery listed on the LOF. Therefore,
NMFS does not consider American eel
to be a target species in the Atlantic
mixed species trap/pot fishery and will
correct this oversight in a future LOF.
NMFS includes this fishery in the 2010
AD to target observer coverage more
specifically to obtain information on sea
turtle interactions and how sea turtles
may be interacting with trap/pot gear,
particularly in waters off of
Massachusetts and waters south of this
area, as sea turtles more commonly
occur in these areas.
North Carolina Inshore Gillnet Fishery
The NC inshore gillnet fishery (94
vessels/persons) targets species
including, but not limited to, southern
flounder, weakfish, bluefish, Atlantic
croaker, striped mullet, spotted seatrout,
Spanish mackerel, striped bass, spot,
red drum, black drum, and shad. This
fishery includes any fishing effort using
any type of gillnet gear, including set
(float and sink), drift, and runaround
gillnet for any target species inshore of
the COLREGS lines in North Carolina.
NMFS includes this fishery on the 2010
AD because the fishery overlaps
spatially with areas used by sea turtles,
often at relatively high densities and
high takes have been previously
documented. A more extensive, longerterm observer program is needed to
adequately assess the extent and impact
of the all components of the inshore
North Carolina gillnet fishery on sea
turtles.
Southeast Atlantic Gillnet Fishery
The Southeast Atlantic gillnet fishery
(779 estimated vessels/persons) targets
finfish including, but not limited to,
king mackerel, Spanish mackerel,
whiting, bluefish, pompano, spot,
croaker, little tunny, bonita, jack
crevalle, cobia, and striped mullet.
NMFS includes this fishery on the 2010
to focus observer coverage during times
and in areas where sea turtles are
known to occur.
Trap/Pot Fisheries
Atlantic Blue Crab Trap/Pot Fishery
The Atlantic blue crab trap/pot
fishery (estimated ≤16,000 vessels/
persons) targets blue crab using pots
baited with fish or poultry typically set
in rows in shallow water. NMFS
includes this fishery on the 2010 AD to
target observer coverage more
specifically to obtain information on sea
turtle bycatch and how sea turtles may
be interacting with trap/pot gear.
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Northeast/Mid-Atlantic American
Lobster Trap/Pot Fishery
The Northeast/Mid-Atlantic American
lobster trap/pot fishery (estimated
13,000 vessels/persons) targets
American lobster primarily with traps,
while 2–3 percent of the target species
is taken by mobile gear (trawls and
dredges). NMFS includes this fishery in
the 2010 AD to target observer coverage
more specifically to obtain information
on sea turtle bycatch and how sea
turtles may be interacting with trap/pot
gear, particularly in waters off of
Massachusetts and waters south of this
area, as sea turtles more commonly
occur in these areas.
Pound Net/Weir/Seine Fisheries
Mid-Atlantic Haul/Beach Seine Fishery
The Mid-Atlantic haul/beach seine
fishery (estimated >221 vessels/persons)
targets striped bass, mullet, spot,
weakfish, sea trout, bluefish, kingfish,
and harvest fish using seines with one
end secured (e.g., swipe nets and long
seines) and seines secured at both ends
or those anchored to the beach and
hauled up on the beach. NMFS includes
this fishery on the 2010 AD based on
suspected interactions with sea turtles
given the nature of the gear and fishing
methodology in addition to effort
overlapping with sea turtle distribution.
In the Chesapeake Bay, the fishery
operates at the same time as historically
elevated sea turtle strandings.
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Mid-Atlantic Menhaden Purse Seine
Fishery
The Mid-Atlantic menhaden purse
seine fishery (22 estimated vessels/
persons) targets menhaden and thread
herring using purse seine gear. NMFS
includes this fishery on the 2010 AD to
focus observer coverage in times and
areas of sea turtle distribution and learn
more about the interactions between
this fishery and sea turtles.
Virginia Pound Net Fishery
The Virginia pound net fishery
(estimated 41 vessels/persons) targets
species including, but not limited to,
croaker, menhaden, mackerel, weakfish,
and spot, using stationary gear in
nearshore Virginia waters, primarily in
the Chesapeake Bay and its tributaries.
NMFS includes this fishery on the 2010
AD to assess interactions between
pound net gear and sea turtles and to
evaluate the effectiveness of the
modified gear. Because some vessels in
this fishery may be too small to carry
observers, NMFS would consider
observing the fishery using both
traditional methods as well as an
alternative platform.
27657
U.S. Mid-Atlantic Mixed Species Stop
Seine/Weir/Pound Net (except the NC
roe mullet stop net) Fishery
The Mid-Atlantic mixed species stop
seine/weir/pound net fishery (estimated
751 vessels/persons) targets several
species, including, but not limited to,
weakfish, striped bass, shark, catfish,
menhaden, flounder, gizzard shad, and
white perch. NMFS includes this fishery
on the 2010 AD to better understand the
nature and extent of these interactions
in the mid-Atlantic.
TABLE 1 – STATE AND FEDERAL COMMERCIAL FISHERIES INCLUDED ON THE 2010 ANNUAL DETERMINATION
Fishery
Years Eligible to Carry Observers
Trawl Fisheries
Atlantic shellfish bottom trawl
2010–2014
Mid-Atlantic bottom trawl
2010–2014
Mid-Atlantic mid-water trawl (including pair trawl)
2010–2014
Southeastern U.S. Atlantic, Gulf of Mexico shrimp trawl
2010–2014
Gillnet Fisheries
CA halibut, white seabass and other species set gillnet (>3.5 in mesh)
2010–2014
CA yellowtail, barracuda, and white seabass drift gillnet (mesh size >3.5 in. and
<14 in.)
2010–2014
Chesapeake Bay inshore gillnet
2010–2014
Long Island inshore gillnet
2010–2014
Mid-Atlantic gillnet
2010–2014
North Carolina inshore gillnet
2010–2014
Northeast sink gillnet
2010–2014
Southeast Atlantic gillnet
2010–2014
Trap/pot Fisheries
Atlantic blue crab trap/pot
2010–2014
Atlantic mixed species trap/pot
2010–2014
Northeast/mid-Atlantic American lobster trap/pot
2010–2014
Pound Net/Weir/Seine Fisheries
2010–2014
Mid-Atlantic menhaden purse seine
2010–2014
U.S. mid-Atlantic mixed species stop seine/weir/pound net (except the NC roe
mullet stop net)
2010–2014
Virginia pound net
hsrobinson on DSK69SOYB1PROD with RULES
Mid-Atlantic haul/beach seine
2010–2014
Classification
The Chief Counsel for Regulation of
the Department of Commerce certified
to the Chief Counsel for Advocacy of the
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Small Business Administration that this
rule would not have a significant
economic impact on a substantial
number of small entities. The factual
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basis leading to the certification is set
forth below.
NMFS has estimated that
approximately 65,940 vessels
participating in 19 fisheries listed in
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Federal Register / Vol. 75, No. 95 / Tuesday, May 18, 2010 / Rules and Regulations
Table 1 would be eligible to carry an
observer if requested. However, NMFS
would only request a fraction of the
total number of participants to carry an
observer based on the sampling protocol
identified for each fishery by regional
observer programs. As noted throughout
this proposed rule, NMFS would select
vessels and focus coverage in times and
areas where fishing effort overlaps with
sea turtle distribution. Due to the
unpredictability of fishing effort, NMFS
cannot determine the specific number of
vessels that would be requested to carry
an observer.
If a vessel is requested to carry an
observer, fishers will not incur any
direct economic costs associated with
carrying that observer. Potential indirect
costs to individual fishers required to
take observers may include: lost space
on deck for catch, lost bunk space, and
lost fishing time due to time needed to
process bycatch data. For effective
monitoring, however, observers will
rotate among a limited number of
vessels in a fishery at any given time
and each vessel within an observed
fishery has an equal probability of being
requested to accommodate an observer.
The potential indirect costs to
individual fishers are expected to be
minimal because observer coverage
would only be required for a small
percentage of an individual vessel’s
total annual fishing time. In addition, 50
CFR 222.404(b) states that an observer
will not be placed on a vessel if the
facilities for quartering an observer or
performing observer functions are
inadequate or unsafe, thereby exempting
vessels too small to accommodate an
observer from this requirement. As a
result of this certification, an initial
regulatory flexibility analysis is not
required and was not prepared.
The requirements to carry an observer
when requested for those fisheries
included on the 2010 AD through this
final rule are included under an existing
collection-of-information that was
approved by the Office of Management
and Budget (OMB) under OMB control
number 0648–0593.
Notwithstanding any other provision
of the law, no person is required to
respond to, nor shall any person be
subject to a penalty for failure to comply
with, a collection of information subject
to the requirements of the Paperwork
Reduction Act, unless that collection of
information displays a currently valid
OMB Control Number.
This final rule has been determined to
be not significant for the purposes of
Executive Order 12866.
An environmental assessment (EA)
was prepared under the National
Environmental Policy Act (NEPA) for
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regulations to implement this observer
requirement in 50 CFR part 222, subpart
D. The EA concluded that implementing
these regulations would not have a
significant impact on the human
environment. This fianl rule would not
make any significant change in the
management of fisheries included on
the AD, and therefore, this final rule
would not change the analysis or
conclusion of the EA. If NMFS takes a
management action, for example,
requiring fishing gear modifications
such as TEDs, NMFS would first
prepare an environmental document as
required under NEPA and specific to
that action.
This final rule would not affect
species listed as threatened or
endangered under the Endangered
Species Act (ESA) or their associated
critical habitat. The impacts of
numerous fisheries have been analyzed
in various biological opinions, and this
final rule would not affect the
conclusions of those opinions.
Including fisheries on the AD is not
considered to be a management action
that would adversely affect threatened
or endangered species. If NMFS takes a
management action, for example,
requiring modifications to fishing gear
and/or practices, NMFS would review
the action for potential adverse affects to
listed species under the ESA.
This final rule would have no adverse
impacts on sea turtles and may have a
positive impact on sea turtles by
improving knowledge of sea turtles and
the fisheries interacting with sea turtles
through information collected from
observer programs.
Literature Cited
Murray, K.T. 2009. Characteristics
and magnitude of sea turtle bycatch in
US mid-Atlantic gillnet gear.
Endangered Species Research 8:211–
224.
National Marine Fisheries Service.
2009. Draft 2009 Marine Mammal Stock
Assessment Reports for the Atlantic
Ocean and Gulf of Mexico.
https://www.nmfs.noaa.gov/pr/pdfs/
sars/ao2009ldraftlappendices.pdf
Dated: May 11, 2010.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
[FR Doc. 2010–11856 Filed 5–17–10; 8:45 am]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 622
[Docket No. 090508900–91414–02]
RIN 0648–AX75
Fisheries of the Caribbean, Gulf of
Mexico, and South Atlantic; SnapperGrouper Fishery of the South Atlantic;
Red Snapper Closure
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Temporary rule; interim
measures extended.
SUMMARY: NMFS issues this temporary
rule to extend the effective date of
interim measures to reduce overfishing
of red snapper in the South Atlantic
implemented by a temporary rule
published by NMFS on December 4,
2009 (74 FR 63673). This temporary rule
extends the closure of the commercial
and recreational fisheries for red
snapper in the exclusive economic zone
(EEZ) of the South Atlantic as requested
by the South Atlantic Fishery
Management Council (Council). The
intended effect of this rule is to reduce
overfishing of red snapper in the South
Atlantic.
DATES: The effective date for the interim
rule published at 74 FR 63673,
December 4, 2009, is extended from
June 3, 2010, through December 5, 2010,
unless NMFS publishes a superseding
document in the Federal Register.
ADDRESSES: Copies of the final
regulatory flexibility analysis (FRFA)
and environmental assessment (EA) may
be obtained from Karla Gore, Southeast
Regional Office, NMFS, 263 13th
Avenue South, St. Petersburg, FL 33701.
FOR FURTHER INFORMATION CONTACT:
Karla Gore, telephone: 727–551–5305.
SUPPLEMENTARY INFORMATION: The
snapper-grouper fishery off the southern
Atlantic states is managed under the
Fishery Management Plan for the
Snapper-Grouper Fishery of the South
Atlantic Region (FMP). The FMP was
prepared by the Council and is
implemented under the authority of the
Magnuson-Stevens Fishery
Conservation and Management Act
(Magnuson-Stevens Act) by regulations
at 50 CFR part 622.
On December 4, 2009, NMFS
published the final temporary rule (74
FR 63673) to implement measures to
establish a closure of the commercial
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Agencies
[Federal Register Volume 75, Number 95 (Tuesday, May 18, 2010)]
[Rules and Regulations]
[Pages 27649-27658]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-11856]
=======================================================================
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 222
[Docket No. 0906181067-0167-02]
RIN 0648-XP96
2010 Annual Determination for Sea Turtle Observer Requirements
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The National Marine Fisheries Service (NMFS) publishes its
final Annual Determination (AD) for 2010, pursuant to its authority
under the Endangered Species Act (ESA). Through this AD, NMFS
identifies commercial fisheries operating in state and Federal waters
in the Atlantic Ocean, Gulf of Mexico, and Pacific Ocean that will be
required to take observers upon NMFS' request. The purpose of observing
identified fisheries is to learn more about sea turtle interactions in
a given fishery, evaluate existing measures to reduce or prevent
prohibited sea turtle takes, and to determine whether additional
measures to implement the prohibition against sea turtle takes may be
necessary. Fisheries identified through this process will remain on the
AD, and therefore required to carry observers upon NMFS' request, for 5
years.
DATES: Effective June 17, 2010.
ADDRESSES: See SUPPLEMENTARY INFORMATION for a listing of all Regional
Offices.
FOR FURTHER INFORMATION CONTACT: Kristy Long, Office of Protected
Resources, 301-713-2322; Ellen Keane, Northeast Region, 978-282-8476;
Dennis Klemm, Southeast Region, 727-824-5312; Elizabeth Petras,
Southwest
[[Page 27650]]
Region, 562-980-3238; Kim Maison, Pacific Islands Region, 808-944-2257.
Individuals who use a telecommunications device for the hearing
impaired may call the Federal Information Relay Service at 1-800-877-
8339 between 8 a.m. and 4 p.m. Eastern time, Monday through Friday,
excluding Federal holidays.
SUPPLEMENTARY INFORMATION:
Availability of Published Materials
Information regarding the Marine Mammal Protection Act (MMPA) List
of Fisheries (LOF) may be obtained at https://www.nmfs.noaa.gov/pr/interactions/lof/ and information regarding Marine Mammal Stock
Assessment Reports may be obtained at https://www.nmfs.noaa.gov/pr/sars/
or from any NMFS Regional Office at the addresses listed below:
NMFS, Northeast Region, 55 Great Republic Drive, Gloucester, MA
01930-2298;
NMFS, Southeast Region, 263 13th Avenue South, St. Petersburg, FL
33701;
NMFS, Southwest Region, 501 W. Ocean Blvd., Suite 4200, Long Beach,
CA 90802-4213; or
NMFS, Pacific Islands Region, Protected Resources, 1601 Kapiolani
Boulevard, Suite 1100, Honolulu, HI 96814-4700.
Purpose of the Sea Turtle Observer Requirement
Under the ESA, 16 U.S.C. 1531 et seq., NMFS has the responsibility
to implement programs to conserve marine life listed as endangered or
threatened. All sea turtles found in U.S. waters are listed as either
endangered or threatened under the ESA. Kemp's ridley (Lepidochelys
kempii), leatherback (Dermochelys coriacea), and hawksbill
(Eretmochelys imbricata) sea turtles are listed as endangered.
Loggerhead (Caretta caretta), green (Chelonia mydas), and olive ridley
(Lepidochelys olivacea) sea turtles are listed as threatened, except
for breeding colony populations of green turtles in Florida and on the
Pacific coast of Mexico and breeding colony populations of olive
ridleys on the Pacific coast of Mexico, which are listed as endangered.
Due to the inability to distinguish between populations of green and
olive ridley turtles away from the nesting beach, NMFS considers these
turtles endangered wherever they occur in U.S. waters. While some sea
turtle populations have shown signs of recovery, many populations
continue to decline.
Incidental take, or bycatch, in fishing gear is one of the main
sources of sea turtle injury and mortality nationwide. Section 9 of the
ESA prohibits the take (including harassing, harming, pursuing,
hunting, shooting, wounding, killing, trapping, capturing, or
collecting or attempting to engage in any such conduct), including
incidental take, of endangered sea turtles. Pursuant to section 4(d) of
the ESA, NMFS has issued regulations extending the prohibition of take,
with exceptions, to threatened sea turtles (50 CFR 223.205 and
223.206). Sections 9 and 11 of the ESA authorize the issuance of
regulations to enforce the take prohibitions. NMFS may grant exceptions
to the take prohibitions with an incidental take statement or an
incidental take permit issued pursuant to ESA section 7 or 10,
respectively. To do so, NMFS must determine that the activity that will
result in incidental take is not likely to jeopardize the continued
existence of the affected listed species. In some cases, NMFS has been
able to make this determination because the fishery is conducted with
modified gear or modified fishing practices that NMFS has been able to
evaluate. However, for some Federal fisheries and most state fisheries,
NMFS has not granted an exception primarily because we lack information
about fishery-turtle interactions. Therefore, any incidental take of
sea turtles in those fisheries is unlawful as it has not been exempted
from the ESA prohibition on take.
The most effective way for NMFS to learn more about sea turtle-
fishery interactions in order to prevent or minimize take is to place
observers aboard fishing vessels. In 2007, NMFS issued a regulation (50
CFR 222.402) to establish procedures through which each year NMFS will
identify, pursuant to specified criteria and after notice and
opportunity for comment, those fisheries in which the agency intends to
place observers (72 FR 43176, August 3, 2007). These regulations
specify that NMFS may place observers on U.S. fishing vessels, either
recreational or commercial, operating in U.S. territorial waters, the
U.S. exclusive economic zone (EEZ), or on the high seas, or on vessels
that are otherwise subject to the jurisdiction of the U.S. Failure to
comply with the requirements under this rule may result in civil or
criminal penalties under the ESA.
NMFS and/or interested cooperating entities will pay the direct
costs for vessels to carry observers. These include observer salary and
insurance costs. NMFS may also evaluate other potential direct costs,
should they arise. Once selected, a fishery will be eligible to be
observed for five years without further action by NMFS. This will
enable NMFS to develop an appropriate sampling protocol to investigate
whether, how, when, where, and under what conditions incidental takes
are occurring; to evaluate whether existing measures are minimizing or
preventing takes; and to determine whether additional measures are
needed to implement ESA take prohibitions and conserve turtles.
Process for Developing an Annual Determination
Pursuant to 50 CFR 222.402, the Assistant Administrator for
Fisheries, NOAA (AA), in consultation with Regional Administrators and
Fisheries Science Center Directors, develops a proposed annual
determination identifying which fisheries are required to carry
observers, if requested, to monitor potential interactions with sea
turtles. NMFS provides an opportunity for public comment on any
proposed determination. The determination is based on the best
available scientific, commercial, or other information regarding sea
turtle-fishery interactions; sea turtle distribution; sea turtle
strandings; fishing techniques, gears used, target species, seasons and
areas fished; or qualitative data from logbooks or fisher reports.
Specifically, this determination is based on the extent to which:
(1) The fishery operates in the same waters and at the same time as
sea turtles are present;
(2) The fishery operates at the same time or prior to elevated sea
turtle strandings; or
(3) The fishery uses a gear or technique that is known or likely to
result in incidental take of sea turtles based on documented or
reported takes in the same or similar fisheries; and
(4) NMFS intends to monitor the fishery and anticipates that it
will have the funds to do so.
The AA used the most recent version of the annually published MMPA
List of Fisheries (LOF) as the comprehensive list of commercial
fisheries for consideration. The LOF includes all known state and
Federal commercial fisheries that occur in U.S. waters. The
classification scheme used for fisheries on the LOF would not be
relevant to this process. Unlike the LOF process, an annual
determination may also include recreational fisheries likely to
interact with sea turtles on the basis of the best available
information.
NMFS consulted with appropriate state and Federal fisheries
officials and other entities to identify which fisheries, both
commercial and recreational, should be considered in the annual
determination. Although the
[[Page 27651]]
comments and recommendations provided to NMFS by states were based upon
the best available information on their fisheries, NMFS received more
recommendations for fisheries to include on the 2010 AD than is
feasible at this time based on the four previously noted criteria (50
CFR 222.402(a)).
The AD is not an exhaustive or comprehensive list of all fisheries
with documented or suspected takes of sea turtles; there are additional
fisheries that NMFS remains concerned about. For these additional
fisheries, NMFS may already be addressing incidental take through
another mechanism (e.g., rulemaking to implement modifications to
fishing gear and/or practices) or will consider adding them to future
annual determinations based on the four previously noted criteria (50
CFR 222.402(a)).
Notice of a final determination, such as the 2010 AD, will be
published in the Federal Register and made in writing to individuals
permitted for each fishery identified for monitoring. NMFS will also
notify state agencies and provide notification through publication in
local newspapers, radio broadcasts, and other means, as appropriate.
Once included in a final determination, a fishery will remain eligible
for observer coverage for five years to enable the design of an
appropriate sampling program and to ensure collection of sufficient
scientific data for analysis. If NMFS determines that more than five
years are needed to obtain sufficient scientific data, NMFS will
include the fishery in the proposed AD again prior to the end of the
fifth year. As part of the 2010 AD, NMFS included, to the extent
practicable, information on the fisheries or gear types to be sampled,
geographic and seasonal scope of coverage, and any other relevant
information. After publication of a final AD, a 30-day delay in
effective date for implementing observer coverage will follow, except
for those fisheries where the AA has determined that there is good
cause pursuant to the Administrative Procedure Act to make the rule
effective without a 30-day delay.
Implementing Observer Coverage in a Fishery Listed on the 2010 Annual
Determination
The design of any observer program for fisheries identified through
the AD process, including how observers will be allocated to individual
vessels, would vary among fisheries, fishing sectors, gear types, and
geographic regions and would ultimately be determined by the individual
NMFS Regional Office, Science Center, and/or observer program. During
the program design, NMFS will be guided by the following standards for
distributing and placing observers among fisheries identified in the AD
and vessels in those particular fisheries:
(1) The requirements to obtain the best available scientific
information;
(2) The requirement that observers be assigned fairly and equitably
among fisheries and among vessels in a fishery;
(3) The requirement that no individual person or vessel, or group
of persons or vessels, be subject to inappropriate, excessive observer
coverage; and
(4) The need to minimize costs and avoid duplication, where
practicable.
Vessels subject to observer coverage under this rule must comply
with observer safety requirements specified at 50 CFR 600.725 and 50
CFR 600.746. Specifically, 50 CFR 600.746(c) requires vessels to
provide adequate and safe conditions for carrying an observer and
conditions that allow for operation of normal observer functions. To
provide such conditions, a vessel must comply with the applicable
regulations regarding observer accommodations (see 50 CFR parts 229,
300, 600, 622, 635, 648, 660, and 679) and possess a current USCG
Commercial Fishing Vessel Safety Examination decal or a USCG
certificate of examination. A vessel that fails to meet these
requirements at the time an observer is to be deployed on the vessel is
prohibited from fishing, 50 CFR 600.746(f), unless NMFS determines that
an alternative platform (e.g., a second vessel) may be used. In any
case, all fishermen on a vessel must cooperate in the operation of
observer functions. Observer programs designed or carried out in
accordance with 50 CFR 222.404 would be required to be consistent with
existing observer-related NOAA policies and regulations, such as those
under the Fair Labor and Standards Act (29 U.S.C. 201 et seq.), the
Service Contract Act (41 U.S.C. 351 et seq.), Observer Health and
Safety regulations (50 CFR 600), and other relevant policies.
Fisheries not included on the 2010 AD may still be observed under a
different authority than the ESA (e.g., MMPA, MSA).
Additional information on observer programs in commercial fisheries
can be found on the NMFS National Observer Program's website: https://www.st.nmfs.gov/st4/nop/; links to individual regional observer
programs may also be found on this website.
Comments and Responses
NMFS received comments from 3 individual members of the public,
Environmental Defense Fund, Oceana, Garden State Seafood Association,
Cape Seafoods, Inc., Lund's Fisheries, Inc., Northern Pelagic Group
LLC, Western Sea Fishing Company, Mid-Atlantic Fishery Management
Council, and the States of Connecticut, Maryland, and New Jersey on the
proposed 2010 AD (74 FR 59508, November 18, 2009). Comments on issues
outside the scope of the AD were noted, but are not responded to in
this final rule.
General Comments
Comment 1: Several commenters support including 19 fisheries on the
2010 AD.
Response: NMFS agrees and includes 19 fisheries on the 2010 AD.
Comment 2: The State of New Jersey inquired whether the fisheries
to be observed listed in Table 1 are in priority order.
Response: Table 1 is somewhat prioritized by gear type (trawl,
gillnet, trap/pot, and pound net/weir/seine); specific fisheries within
those gear types are alphabetized. The order of those gear types
represents NMFS' current priorities under the NMFS' Strategy for Sea
Turtle Conservation and Recovery in Relation to Atlantic Ocean and Gulf
of Mexico Fisheries (``Strategy''). Fisheries operating in the Pacific
Ocean will be considered similarly. However, NMFS' Regional Observer
Programs are implemented somewhat independently based on several
factors including available funding, staff resources, the number of
certified observers in a given region, etc. Therefore, NMFS will
consider all of these factors when deciding which fisheries to observe
in a given year. For example, increasing coverage within existing
observer programs may be more feasible than beginning a new program in
a given year based on available funding and staff resources in a
particular region.
Comment 3: Cape Seafoods, Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association inquired how and when fisheries are removed from
the AD. The commenters suggest that there be a process outlined in this
final rule for removing fisheries before the 5 years expire.
Response: The amount of time that fisheries remain on the AD was
the subject of the previous rulemaking that implemented the observer
requirement (72 FR 43176, August 3, 2007); this rulemaking does not
amend those regulations or implement new regulations. The regulations
at 50 CFR 222.403(a) specify that once selected, a fishery remains
eligible for observer coverage for five years.
[[Page 27652]]
Comment 4: Cape Seafoods, Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association suggest adding a criterion for including fisheries
on the AD that considers past observer coverage.
Response: The criteria that NMFS considers when proposing to
include a fishery on the AD were the subject of the previous rulemaking
that implemented the observer requirement (72 FR 43176, August 3,
2007); this rulemaking does not amend those regulations or implement
new regulations.
Comment 5: The State of Connecticut notes that the report from the
2008 Observer Workshop includes a statement about using state observers
under NMFS' authority to implement this observer requirement and they
would like to have state observers certified for this purpose.
Response: Since the workshop in 2008, NMFS has determined that the
regulations in 50 CFR 222.402 provide authorization only for Federal
observer programs implemented by NMFS. The State may be able to act as
the Observer Service Provider and enter into an agreement with NMFS
contingent upon certification of those observers by NMFS (i.e., those
state observers are NMFS-certified).
Comment 6: Cape Seafoods, Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association suggests that broad gear categories do not pose
similar risks to sea turtles and recommends that fisheries be examined
on a case-by-case basis for temporal/spatial overlap with turtle
distribution, while accounting for regional fishing practices and past/
current observer coverage.
Response: The universe of commercial fisheries considered for the
Annual Determination is based on the MMPA LOF. If the LOF defines a
fishery based on broad gear type, NMFS must also use that same fishery
on the Annual Determination. If the commenters have suggestions for re-
defining fisheries on the MMPA LOF, they should consider commenting
during the 2011 LOF process. See Comments on Observer Programs below
for additional information on how past observer coverage is factored
into sampling designs.
Comment 7: Cape Seafoods, Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association inquired how this observer requirement would yield
statistically rigorous information when statistically valid information
or accurate data on the status and trends of sea turtles has not been
provided.
Response: This comment appears to be directed at the rule
promulgated by NMFS on August 3, 2007, codified at 50 CFR Part 222
Subpart D, and is thus outside the scope of this rulemaking. However,
NMFS responds to clarify that, as stated in the preamble to that
rulemaking: ``Sampling designs for all NMFS observer programs are
developed to provide statistically valid information and to produce
results that will contribute to the body of best available science. The
sampling design will vary depending on many factors, including the
fishery to be observed, the spatial and temporal variability in the
fishery and species observed, and the overall goals of the observer
program. Once a fishery is selected for observer coverage, a sampling
design will be developed to yield statistically valid results.'' [72 FR
43176, August 3, 2007]
Regardless of the data available on the status and trends of sea
turtles, this program will collect statistically valid information on
sea turtle takes. NMFS continues to work to better understand the
status and trends of sea turtle populations, including through survey
efforts, population modeling, and status reviews.
Comment 8: Cape Seafoods, Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association further inquired how bycatch rates and estimates
would be applied during ESA section 7 and 10 consultations as well as
broad-based gear regulations.
Response: This comment is beyond the scope of this rulemaking. The
preamble to the rule codified at 50 CFR Part 222 Subpart D describes
how the information gathered will be used (72 FR 43176, August 3,
2007). Because data have not yet been collected nor analyzed, NMFS can
not now identify what, if any, management actions it might take in
response to those data.
Comments on Observer Programs
Comment 9: Environmental Defense Fund recommends using new
technologies, including video monitoring to eliminate observer bias,
increase level of monitoring (as it becomes more cost effective) and
monitor unobservable vessels.
Response: New technologies for monitoring fisheries (commonly
referred to as ``electronic monitoring'' or EM) offer many benefits of
interest to NMFS. However, their efficacy in meeting monitoring
objectives varies by fishery and monitoring goal. EM studies, including
video monitoring, are ongoing in many NMFS regions, and the results are
promising. The ability of these technologies to meet monitoring
objectives has primarily been evaluated in experimental situations;
many questions still remain as to their efficacy and true cost. NMFS
generally supports the use of EM to augment at-sea observer coverage,
and fully supports the use of EM, as well as other alternative
monitoring methods, to cover unobservable vessels. NMFS will continue
to work through its cooperative research and fisheries observer
programs to evaluate how EM technology may be used to supplement
observer programs, including those implemented under the AD.
Comment 10: The State of New Jersey requested training in observer
protocols for state personnel to augment NMFS coverage in state waters
under State authority and increase effectiveness.
Response: The Northeast Fisheries Observer Program (NEFOP) has
helped individual states develop their own state fisheries observer
programs, and will continue to do so as long as the demand doesn't
compromise the training needs of NEFOP. The support NEFOP provides
includes training, logs, manuals, protocols and entry screens.
Comment 11: The State of New Jersey inquired how observer coverage
will be allocated across fisheries and requested that the State be
consulted each year during the vessel selection process.
Response: Observer coverage is allocated in proportion to fishing
effort by time/area. All active vessels, indentified for observer
coverage within a particular time/area, may be randomly selected.
Current NEFOP protocols prohibit repeat trips on the same vessel,
during a 30 day period, if other vessels are active and have not been
selected. NEFOP attempts to ensure that observer coverage is fair and
equitable, without overburdening a particular fisherman or fishery.
NEFOP posts the sea day schedule on the following website: https://www.nefsc.noaa.gov/femad/fsb. This website provides the chance for all
interested parties to review the planned coverage. NEFOP would welcome
the opportunity to work with individual states when developing a list
of vessels to be selected for that proposed coverage.
Comment 12: Cape Seafoods, Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association inquired how NMFS will implement the requirements
in a way that no fisherman or group of fishermen will be expected to
carry excessive observer coverage. Further, Garden State
[[Page 27653]]
Seafood Association believes that NJ fishermen have been overburdened
with an excessive share of observer training trips/coverage (e.g., 72
trips in 2005).
Response: As previously described, NEFOP makes every legitimate
attempt to not overburden a particular fisherman or fishery. Days are
allocated in proportion to fishing effort by time/area. From 2000 to
2005, the NEFOP grew from 1,200 sea days per year to 12,000 sea days
per year; increasing from 12 to 120 observers. That increase
necessitated additional training trips. Training trips require that an
experienced observer shadow a new observer until they are fully
certified in all sampling protocols. Gillnet sampling protocols, per
NEFSC scientists conducting harbor porpoise bycatch analysis, require
observers to observe the net for harbor porpoise ``fall outs'' during
retrieval, instead of sampling discarded fish. These trips are referred
to as ``limited'' gillnet trips because of the limited sampling of
fish. All of the gillnet days on the NEFOP sea day schedule for
protected species are ``limited'' days. This includes both New England
and mid-Atlantic areas. In addition to these ``limited'' gillnet days,
scientists conducting fish stock assessments also populated the sea day
schedule with gillnet days, but unlike the ``limited'' days, complete
sampling of all discards was required. The majority of these
``complete'' days were assigned to areas in New Jersey and north. Prior
to December 2005, in order to provide the best training trips possible,
new observers from southern ports were often sent to New Jersey, or
ports farther north, for those important training trips. This resulted
in proportionally more training trips occurring in New Jersey. Once
this problem was brought to the attention of NEFOP, protocols were
changed so that new observers, during their training trips, could use
``complete'' sampling protocols regardless of the port used for
training. This change was made in December 2005, and since then NEFOP
has not received any reports that this issue continues to be a problem.
Comment 13: Cape Seafoods, Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association expressed concern about the competing needs (e.g.,
population dynamics, food habits, protected species, fisheries
management, etc.) for a given observer program and how NMFS intends to
balance those needs with observer program design/implementation. The
commenters also note that the proposed 2010 AD indicates that the
program design could be the responsibility of a regional office,
science center, or observer program. The commenters suggest that clear
lines of responsibility should be placed on program design/
implementation.
Response: Within each of the six NMFS Regional Observer Programs,
the responsibility for observer program design and implementation is
clearly defined. Manual and protocol revisions occur regularly based on
the changing needs of end users (e.g., NMFS managers). For example,
NEFOP works closely with all end users to ensure that the data
collected by observers is relevant and meets their needs. Those needs,
for example, could include compliance monitoring, data collection for
regulatory development, or data collection for stock assessments. To
date, NEFOP has been able to successfully balance the needs of all end
users.
Comment 14: Cape Seafoods, Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association suggested that NMFS consider social and economic
burdens of sea turtle observer coverage with respect to total observer
coverage.
Response: See Response to Comment 11 and the Classification section
below.
Comment 15: One commenter inquired whether minimum standards for
selecting a vessel, in each of the fisheries, to carry an observer have
been identified. The commenter notes potential for introducing bias and
suggests NMFS Observer Programs develop methods for reducing the number
of unobservable vessels.
Response: With the exception of certain safety requirements (e.g.,
possessing a current U.S. Coast Guard commercial fishing vessel safety
decal), minimum national standards for vessel selection do not exist.
Regional observer programs perform routine analyses to diagnose and
correct for bias in vessel selection. A 2006 NMFS workshop (report
available from: https://www.st.nmfs.noaa.gov/st4/nop/workshops.html)
reviewed vessel selection procedures and documented analytical methods
and tools that could be used to assess the occurrence and magnitude of
bias. Workshop participants identified alternative selection methods
that could reduce or eliminate sources of bias, such as using
alternative platforms or electronic monitoring to address unobservable
vessels.
Comments on Trawl Fisheries
Comment 16: The Mid-Atlantic Fishery Management Council suggested
removing Illex from the list of species targeted with flynets because
while they are included in the mid-Atlantic bottom trawl general
category, the Illex fishery is not prosecuted using flynets.
Response: The flynet fishery description in the proposed 2010 AD is
based on the fishery as defined under the Marine Mammal Protection Act
(LOF). NMFS will consider revising the characterization of the flynet
fishery in a future LOF.
Comment 17: Cape Seafoods Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association recommend removing the mid-Atlantic mid-water trawl
(including pair trawl) for mackerel from the 2010 AD as optimum
mackerel trawl fishing occurs in areas where the sea surface
temperature is less than 7 degrees Celsius. The commenters note that
this temperature regime is not in the range one would expect sea
turtles to normally thrive.
Response: Sea turtles are poikilotherms whose internal body
temperature is affected by the ambient environment. They undertake
routine migrations along the coast limited by seasonal water
temperatures. Loggerheads have been observed in waters with surface
temperatures of 7[deg] to 30[deg] C, but water temperatures
[gteqt]11[deg] C are most favorable (Shoop and Kenney 1992; Epperly et
al., 1995). During the CETAP aerial survey of the outer continental
shelf from Cape Hatteras, North Carolina, to Cape Sable, Nova Scotia,
leatherbacks were sighted in waters within a sea surface temperature
range similar to that observed for loggerheads; from 7[deg]-27.2[deg]
C. However, leatherbacks appear to have a greater tolerance for colder
waters in comparison to loggerhead sea turtles since more leatherbacks
were found at lower temperatures (Shoop and Kenney 1992).
As defined on the LOF, the mid-water trawl fishery for Atlantic
mackerel is one component of the overall mid-Atlantic mid-water trawl
(including pair trawl) fishery. This fishery targets Atlantic mackerel,
chub mackerel, and other miscellaneous pelagic species (e.g., Atlantic
herring). The component of the fishery targeting mackerel uses the same
gear type and fishing practices as the rest of the fishery targeting
other species. Therefore, NMFS is including this fishery on the 2010 AD
to more adequately observe this gear type in areas and during times
where it overlaps with sea turtle distribution.
Comments on Gillnet Fisheries
Comment 18: The State of Connecticut provided information on
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the Long Island Sound commercial gillnet fishery operating in CT
waters. The State noted that there have been less than 19 active fixed
gillnetters operating during the months of May through October, no
interactions with sea turtles have been documented, and there were a
limited number of sea turtle strandings in CT waters (n=12) from 1998
to 2004. The commenter states that it is unlikely that there are enough
turtles present in CT waters and likely to be at risk to justify
observer coverage in this fishery. The commenter also suggests that
monitoring this fishery would not contribute to meaningful information
on sea turtle bycatch.
Response: The portion of the Long Island Sound inshore gillnet
fishery operating in CT waters is one component of the Long Island
Sound inshore gillnet fishery as defined on the LOF. The fishery
includes all gillnet fisheries setting nets west of a line from the
north fork of the eastern end of Long Island, NY (Orient Point to Plum
Island to Fisheries Island) to Watch Hill, RI (59 FR 43703, August 25,
1994). Northeast waters are an important developmental habitat for
hard-shelled sea turtles and sea turtles occur in Long Island Sound. As
described in the proposed rule, sea turtles are vulnerable to
entanglement and drowning in gillnets. Past observer coverage in this
fishery is limited to a small number of federally observed trips.
Therefore, NMFS is including this fishery on the 2010 AD to better
understand this fishery and how it may impact sea turtles. NMFS will
consider information on sea turtle distribution and the spatial and
temporal extent of gillnet fisheries operating in Long Island Sound in
designing an appropriate sampling program for this fishery.
Comment 19: Garden State Seafood Association recommends excluding
NJ-based vessels that target bluefish and croaker in the Mid-Atlantic
gillnet fishery because there were 179 trips observed between 2000 and
2005 and no sea turtle takes were documented.
Response: Fisheries observers in the mid-Atlantic have documented
take of loggerhead, green, Kemp's ridley, and leatherback turtles in
sink gillnet gear from Cape Cod to North Carolina. Observed
interactions have occurred on trips targeting a variety of species,
including bluefish and Atlantic croaker. From 1995-2006, the average
annual bycatch estimate of loggerheads captured in mid-Atlantic sink
gillnet gear was 350 turtles (Murray 2009). Bycatch rates were
correlated with latitude, sea surface temperature, and mesh size.
Highest predicted bycatch rates occurred in warm waters of the southern
mid-Atlantic, in large-mesh (>17.8 cm) gillnet gear (Murray 2009).
Gillnet fisheries, including those targeting bluefish and croaker,
that overlap with sea turtle distribution have the potential to take
sea turtles.
Typically, observer coverage is allocated in proportion to fishing
effort, by month and port, with vessels selected randomly for coverage.
Vessels are selected based on gear type, not target species. If the
majority of the gillnet vessels fishing out of a particular port
targeted bluefish, the data should reflect that.
To better understand the interactions of these fisheries with sea
turtles, NMFS is including the mid-Atlantic gillnet fishery on the 2010
AD to focus observer coverage during times and areas where sea turtles
are known to occur. Information on sea turtle distribution and the
spatial and temporal extent of these fisheries will be considered in
designing an appropriate sampling program for the fishery.
Comment 20: Oceana recommended including all Gulf of Mexico and
Caribbean gillnet fisheries on the 2010 AD because of similarities to
other gillnet fisheries as well as the large number of participants.
Response: NMFS recognizes that gillnet fisheries in areas other
than those identified in the first AD may pose similar issues for sea
turtles. However, the regulations implementing this observer
requirement at 50 CFR 222.402 specifically state that the annual
determination will be based on the extent to which: (1) The fishery
operates in the same waters and at the same time as sea turtles are
present; (2) The fishery operates at the same time or prior to elevated
sea turtle strandings; or (3) The fishery uses a gear or technique that
is known or likely to result in incidental take of sea turtles based on
documented or reported takes in the same or similar fisheries; and (4)
NMFS intends to monitor the fishery and anticipates that it will have
the funds to do so. Although many fisheries meet one or more of the
first three requirements, NMFS must also consider the fourth criterion,
which is dependent upon available agency resources. Given the agency's
current resources for implementing this program, NMFS is not including
any gillnet fisheries in the Gulf of Mexico or Caribbean on the 2010
AD. However, this is an annual process and NMFS will consider including
additional fisheries on future ADs based upon the aforementioned
criteria.
Comments on Trap/Pot Fisheries
Comment 21: The State of Connecticut provided information on the
commercial lobster pot fishery in Connecticut and a description of the
state monitoring program. Specifically, since 1982, the CT Department
of Environmental Protection's Marine Fisheries Division has observed
13,693 multi-trap trawl hauls on 643 commercial lobster trips in Long
Island Sound. During the program, a single take of a sea turtle was
documented in August 2009; a leatherback turtle was observed entangled
in a vertical line.
Response: NMFS appreciates receiving detailed information on the
monitoring program and CT commercial lobster pot fishery. This fishery
is one component of the overall Northeast/Mid-Atlantic American Lobster
Trap/Pot fishery, which operates from Maine to New Jersey and may
extend as far south as Cape Hatteras, NC. As noted by the commenter and
described in the proposed rule (74 FR 59508, November 18, 2009), sea
turtles are known to become entangled in the end lines (also called
vertical lines) of trap/pot gear. There have also been anecdotal
reports that sea turtles may interact with the trap/pot itself. NMFS
currently has only limited data on sea turtle bycatch in this fishery.
NMFS is including this fishery, focusing on waters south of
Massachusetts where sea turtles more commonly occur, on the 2010 AD to
obtain information on sea turtle bycatch and how turtles may interact
with the gear. The information provided will be considered in designing
an appropriate sampling program for this fishery.
Comments on Longline Fisheries
Comment 22: Oceana recommends including all longline fisheries,
both pelagic and bottom longlines, on the 2010 AD. Specifically, the
commenter noted the need for additional observer coverage in the Gulf
of Mexico reef fish bottom longline fishery as well as new observer
programs for the Northeast/mid-Atlantic bottom longline, Caribbean
snapper grouper and other bottom longline fisheries.
Response: The purpose of the sea turtle observer requirement and
the AD is ultimately to implement ESA sections 9 and 4(d), which
prohibit the incidental take of endangered and threatened sea turtles,
respectively. Another purpose of the AD is to learn more about sea
turtle-fishery interactions in the identified fisheries in order to
have information necessary to provide exemptions to the take
prohibitions, consistent with ESA sections 4(d), 7 and 10, if warranted
for certain fisheries.
NMFS did not include any pelagic longline fisheries on the 2010 AD
because all commercial pelagic longline
[[Page 27655]]
fisheries as included on the MMPA LOF are currently observed for sea
turtles and incidental takes authorized. Similarly, the Gulf of Mexico
reef fish bottom longline fishery is currently observed for sea turtles
and takes authorized. Therefore, including these fisheries on the 2010
AD would be duplicative at this time.
NMFS evaluated the aforementioned criteria in 50 CFR 222.402 and
determined that the agency could not satisfy the fourth criterion at
this time with regard to including the other bottom longline fisheries
recommended by the commenter. However, this is an annual process and
NMFS will consider including additional fisheries, including longline
fisheries, on future ADs.
Comments on Recreational Fisheries
Comment 23: Cape Seafoods Inc., Lund's Fisheries, Inc., Northern
Pelagic Group LLC, Western Sea Fishing Company, and Garden State
Seafood Association suggests noting that recreational fisheries are
responsible for sea turtle deaths and recommends that NMFS specify a
clear process for including recreational fisheries on the AD.
Specifically, they recommend using the new recreational fishing
registry implemented in January 2009 to identify fisheries.
Response: NMFS recognizes that recreational fisheries may also
incidentally take sea turtles and, therefore, included recreational
fisheries under the observer requirement at 50 CFR 222.401.
NMFS appreciates the commenter's suggestion to use the recreational
fishing registry and will consider including recreational fisheries on
future ADs.
Comment 24: Oceana recommended including recreational fisheries on
the 2010 AD.
Response: NMFS considered recreational fisheries in developing the
proposed 2010 AD, but the agency did not feel we had enough information
to develop an observer program. Further, NMFS determined that the
agency could not satisfy the criterion at 50 CFR 222.402(a)(4) required
to include a fishery on the AD. As noted in the response to Comment 23,
NMFS will use the information from the recreational fishing registry,
along with other information from the Marine Recreational Information
Program, to obtain the necessary information to consider including
specific recreational fisheries on a future AD.
Addition of Fisheries on the 2010 Annual Determination
NMFS is including 19 fisheries (17 in the Atlantic Ocean and Gulf
of Mexico and 2 in the Pacific Ocean) on the 2010 AD. These 19
fisheries, described below and listed in Table 1, represent several
gear types, including trawl, gillnet, trap/pot, and pound net/weir/
seine. For a complete description of the information and state
recommendations NMFS used in developing the 2010 AD, please see the
proposed rule (74 FR 59508, November 18, 2009).
Trawl Fisheries
Based on the information provided by states and the best available
scientific information, NMFS includes the following trawl fisheries on
the 2010 AD.
Atlantic Shellfish Bottom Trawl Fishery
The Atlantic shellfish bottom trawl fishery (estimated 972 vessels/
persons) encompasses the calico scallop trawl, crab trawl, Georgia/
South Carolina/Maryland whelk trawl, Gulf of Maine/Mid-Atlantic sea
scallop trawl, and Gulf of Maine northern shrimp trawl (71 FR 2006,
January 4, 2006). This fishery extends from Maine through Florida. NMFS
is particularly interested in observing this fishery in waters off of
Massachusetts and south as sea turtles more commonly occur in this
area. NMFS includes this fishery on the 2010 AD based on documented
interactions with sea turtles in this and other bottom trawl fisheries
and the need to obtain more information on the interactions in this
fishery.
Mid-Atlantic Bottom Trawl Fishery
Bottom otter trawl nets include a variety of net types, including
flynets, which are high profile trawls. The ``Mid-Atlantic bottom trawl
fishery'' as described in this proposed AD includes both the mid-
Atlantic bottom trawl fishery and the mid-Atlantic flynet fishery as
defined on the LOF.
The Mid-Atlantic bottom trawl fishery (estimated <1,000 vessels/
persons), as defined on the LOF, uses bottom trawl gear to target
species including, but not limited to, bluefish, croaker, monkfish,
summer flounder (fluke), winter flounder, silver hake (whiting), spiny
dogfish, smooth dogfish, scup, and black sea bass. The fishery occurs
year-round from Cape Cod, MA, to Cape Hatteras, NC, in waters west of
72[deg] 30' W. long. and north of a line extending due east from the
North Carolina/South Carolina border.
The Mid-Atlantic flynet fishery (estimated 21 vessels/persons), as
defined on the LOF, is a multi-species fishery composed of nearshore
and offshore components that operate along the east coast of the mid-
Atlantic United States. The nearshore fishery operates from October to
April inside of 30 fathoms (180 ft; 55 m) from New Jersey to North
Carolina. This nearshore fishery targets Atlantic croaker, weakfish,
butterfish, harvestfish, bluefish, menhaden, striped bass, kingfish
species, and other finfish species. The offshore component operates
from November to April outside of 30 fathoms (180 ft; 55 m) from the
Hudson Canyon off New York, south to Hatteras Canyon off North
Carolina. These deeper water fisheries target bluefish, Atlantic
mackerel, Loligo squid, black sea bass, and scup (72 FR 7382, February
15, 2007).
NMFS includes this fishery on the 2010 AD to more adequately
observe this gear type where and when it overlaps with sea turtle
distribution.
Mid-Atlantic Mid-water Trawl (including pair trawl) Fishery
The Mid-Atlantic mid-water trawl fishery (estimated 620 vessels/
persons) primarily targets Atlantic mackerel, chub mackerel, and
miscellaneous other pelagic species. NMFS includes this fishery on the
2010 AD to more adequately observe this gear type in areas and during
times where it overlaps with sea turtle distribution.
Southeastern U.S. Atlantic, Gulf of Mexico Shrimp Trawl Fishery
The Southeastern U.S. Atlantic, Gulf of Mexico shrimp trawl fishery
(estimated >18,000 vessels/persons) targets shrimp using various types
of trawls; NMFS would focus on the component of the fishery that uses
skimmer trawls for the 2010 AD. Skimmer trawls are used primarily in
inshore/inland shallow waters (typically less than 20 ft (6.1 m)) to
target shrimp. NMFS is including the Southeastern U.S. Atlantic, Gulf
of Mexico shrimp trawl fishery, to focus observer coverage in the
component of the fishery that uses skimmer trawls, on the 2010 AD.
Gillnet Fisheries
CA Halibut, White Seabass and Other Species Set Gillnet Fishery (>3.5
in mesh)
The CA halibut, white seabass, and other species set gillnet
fishery (estimated 58 vessels/persons) targets halibut, white seabass,
and other species from the U.S.-Mexico border north to Monterey Bay
using 200 fathom (1,200 ft; 366 m) gillnet with a stretch mesh size of
8.5 in (31.6 cm). NMFS includes this fishery on the 2010 AD because it
[[Page 27656]]
operates in the same waters that turtles are known to occur and this
gear type is known to result in the incidental take of sea turtles
based on documented takes in similar fisheries.
CA Yellowtail, Barracuda, and White Seabass Drift Gillnet Fishery (mesh
size >3.5 in. and <14 in.)
The CA yellowtail, barracuda, and white seabass drift gillnet
fishery (24 vessels/persons) targets primarily yellowtail and white
seabass, and secondarily barracuda, with target species typically
determined by market demand on a short-term basis. NMFS includes this
fishery on the 2010 AD because it operates in the same waters that
turtles are known to occur and this gear type is known to result in the
incidental take of sea turtles based on documented takes in similar
fisheries.
Chesapeake Bay Inshore Gillnet Fishery
The Chesapeake Bay inshore gillnet fishery (estimated 45 vessels/
persons) targets menhaden and croaker using gillnet gear with mesh
sizes ranging from 2.75-5 in (7-12.7 cm), depending on the target
species. NMFS includes this fishery on the 2010 AD because sea turtles
are known to occur in the same areas where the fishery operates, takes
have been previously documented in similar gear, and the fishery
operates during a period of high sea turtle strandings.
Long Island Inshore Gillnet Fishery
The Long Island Sound inshore gillnet fishery (estimated 20
vessels/persons) includes all gillnet fisheries setting nets west of a
line from the north fork of the eastern end of Long Island, NY (Orient
Point to Plum Island to Fishers Island) to Watch Hill, RI (59 FR 43703,
August 25, 1994). NMFS includes this fishery in the 2010 AD because sea
turtles are known to occur in the same areas where the fishery operates
and takes have been documented in similar gear types.
Mid-Atlantic Gillnet Fishery
The Mid-Atlantic gillnet fishery (estimated 7,596 vessels/persons)
targets monkfish, spiny dogfish, smooth dogfish, bluefish, weakfish,
menhaden, spot, croaker, striped bass, large and small coastal sharks,
Spanish mackerel, king mackerel, American shad, black drum, skate spp.,
yellow perch, white perch, herring, scup, kingfish, spotted seatrout,
and butterfish. NMFS includes this fishery on the 2010 AD to focus
observer coverage during times and in areas where sea turtles are known
to occur.
Northeast Sink Gillnet Fishery
The Northeast sink gillnet fishery (estimated >6,455 vessels/
persons) targets Atlantic cod, haddock, pollock, yellowtail flounder,
winter flounder, witch flounder, American plaice, windowpane flounder,
spiny dogfish, monkfish, silver hake, red hake, white hake, ocean pout,
skate spp, mackerel, redfish, and shad. NMFS includes this fishery on
the 2010 AD to focus observer coverage during times and in areas where
sea turtles are known to occur, particularly in waters off
Massachusetts and waters south of this area.
North Carolina Inshore Gillnet Fishery
The NC inshore gillnet fishery (94 vessels/persons) targets species
including, but not limited to, southern flounder, weakfish, bluefish,
Atlantic croaker, striped mullet, spotted seatrout, Spanish mackerel,
striped bass, spot, red drum, black drum, and shad. This fishery
includes any fishing effort using any type of gillnet gear, including
set (float and sink), drift, and runaround gillnet for any target
species inshore of the COLREGS lines in North Carolina. NMFS includes
this fishery on the 2010 AD because the fishery overlaps spatially with
areas used by sea turtles, often at relatively high densities and high
takes have been previously documented. A more extensive, longer-term
observer program is needed to adequately assess the extent and impact
of the all components of the inshore North Carolina gillnet fishery on
sea turtles.
Southeast Atlantic Gillnet Fishery
The Southeast Atlantic gillnet fishery (779 estimated vessels/
persons) targets finfish including, but not limited to, king mackerel,
Spanish mackerel, whiting, bluefish, pompano, spot, croaker, little
tunny, bonita, jack crevalle, cobia, and striped mullet. NMFS includes
this fishery on the 2010 to focus observer coverage during times and in
areas where sea turtles are known to occur.
Trap/Pot Fisheries
Atlantic Blue Crab Trap/Pot Fishery
The Atlantic blue crab trap/pot fishery (estimated >16,000 vessels/
persons) targets blue crab using pots baited with fish or poultry
typically set in rows in shallow water. NMFS includes this fishery on
the 2010 AD to target observer coverage more specifically to obtain
information on sea turtle bycatch and how sea turtles may be
interacting with trap/pot gear.
Atlantic Mixed Species Trap/Pot Fishery
The Atlantic mixed species trap/pot fishery (unknown number of
vessels/persons) targets species including, but not limited to,
hagfish, shrimp, conch/whelk, red crab, Jonah crab, rock crab, black
sea bass, scup, tautog, cod, haddock, pollock, redfish (ocean perch),
white hake, spot, skate, catfish, and stone crab. This fishery as
defined on the MMPA LOF also includes American eel as a target species;
however, there is also a Category III American eel trap/pot fishery
listed on the LOF. Therefore, NMFS does not consider American eel to be
a target species in the Atlantic mixed species trap/pot fishery and
will correct this oversight in a future LOF. NMFS includes this fishery
in the 2010 AD to target observer coverage more specifically to obtain
information on sea turtle interactions and how sea turtles may be
interacting with trap/pot gear, particularly in waters off of
Massachusetts and waters south of this area, as sea turtles more
commonly occur in these areas.
Northeast/Mid-Atlantic American Lobster Trap/Pot Fishery
The Northeast/Mid-Atlantic American lobster trap/pot fishery
(estimated 13,000 vessels/persons) targets American lobster primarily
with traps, while 2-3 percent of the target species is taken by mobile
gear (trawls and dredges). NMFS includes this fishery in the 2010 AD to
target observer coverage more specifically to obtain information on sea
turtle bycatch and how sea turtles may be interacting with trap/pot
gear, particularly in waters off of Massachusetts and waters south of
this area, as sea turtles more commonly occur in these areas.
Pound Net/Weir/Seine Fisheries
Mid-Atlantic Haul/Beach Seine Fishery
The Mid-Atlantic haul/beach seine fishery (estimated >221 vessels/
persons) targets striped bass, mullet, spot, weakfish, sea trout,
bluefish, kingfish, and harvest fish using seines with one end secured
(e.g., swipe nets and long seines) and seines secured at both ends or
those anchored to the beach and hauled up on the beach. NMFS includes
this fishery on the 2010 AD based on suspected interactions with sea
turtles given the nature of the gear and fishing methodology in
addition to effort overlapping with sea turtle distribution. In the
Chesapeake Bay, the fishery operates at the same time as historically
elevated sea turtle strandings.
[[Page 27657]]
Mid-Atlantic Menhaden Purse Seine Fishery
The Mid-Atlantic menhaden purse seine fishery (22 estimated
vessels/persons) targets menhaden and thread herring using purse seine
gear. NMFS includes this fishery on the 2010 AD to focus observer
coverage in times and areas of sea turtle distribution and learn more
about the interactions between this fishery and sea turtles.
Virginia Pound Net Fishery
The Virginia pound net fishery (estimated 41 vessels/persons)
targets species including, but not limited to, croaker, menhaden,
mackerel, weakfish, and spot, using stationary gear in nearshore
Virginia waters, primarily in the Chesapeake Bay and its tributaries.
NMFS includes this fishery on the 2010 AD to assess interactions
between pound net gear and sea turtles and to evaluate the
effectiveness of the modified gear. Because some vessels in this
fishery may be too small to carry observers, NMFS would consider
observing the fishery using both traditional methods as well as an
alternative platform.
U.S. Mid-Atlantic Mixed Species Stop Seine/Weir/Pound Net (except the
NC roe mullet stop net) Fishery
The Mid-Atlantic mixed species stop seine/weir/pound net fishery
(estimated 751 vessels/persons) targets several species, including, but
not limited to, weakfish, striped bass, shark, catfish, menhaden,
flounder, gizzard shad, and white perch. NMFS includes this fishery on
the 2010 AD to better understand the nature and extent of these
interactions in the mid-Atlantic.
Table 1 - State and Federal Commercial Fisheries included on the 2010 Annual Determination
----------------------------------------------------------------------------------------------------------------
Fishery Years Eligible to Carry Observers
----------------------------------------------------------------------------------------------------------------
Trawl Fisheries
----------------------------------------------------------------------------------------------------------------
Atlantic shellfish bottom trawl 2010-2014
----------------------------------------------------------------------------------------------------------------
Mid-Atlantic bottom trawl 2010-2014
----------------------------------------------------------------------------------------------------------------
Mid-Atlantic mid-water trawl (including pair trawl) 2010-2014
----------------------------------------------------------------------------------------------------------------
Southeastern U.S. Atlantic, Gulf of Mexico shrimp trawl 2010-2014
----------------------------------------------------------------------------------------------------------------
Gillnet Fisheries
----------------------------------------------------------------------------------------------------------------
CA halibut, white seabass and other species set gillnet 2010-2014
(>3.5 in mesh)
----------------------------------------------------------------------------------------------------------------
CA yellowtail, barracuda, and white seabass drift 2010-2014
gillnet (mesh size >3.5 in. and <14 in.)
----------------------------------------------------------------------------------------------------------------
Chesapeake Bay inshore gillnet 2010-2014
----------------------------------------------------------------------------------------------------------------
Long Island inshore gillnet 2010-2014
----------------------------------------------------------------------------------------------------------------
Mid-Atlantic gillnet 2010-2014
----------------------------------------------------------------------------------------------------------------
North Carolina inshore gillnet 2010-2014
----------------------------------------------------------------------------------------------------------------
Northeast sink gillnet 2010-2014
----------------------------------------------------------------------------------------------------------------
Southeast Atlantic gillnet 2010-2014
----------------------------------------------------------------------------------------------------------------
Trap/pot Fisheries
----------------------------------------------------------------------------------------------------------------
Atlantic blue crab trap/pot 2010-2014
----------------------------------------------------------------------------------------------------------------
Atlantic mixed species trap/pot 2010-2014
----------------------------------------------------------------------------------------------------------------
Northeast/mid-Atlantic American lobster trap/pot 2010-2014
----------------------------------------------------------------------------------------------------------------
Pound Net/Weir/Seine Fisheries
----------------------------------------------------------------------------------------------------------------
Mid-Atlantic haul/beach seine 2010-2014
----------------------------------------------------------------------------------------------------------------
Mid-Atlantic menhaden purse seine 2010-2014
----------------------------------------------------------------------------------------------------------------
U.S. mid-Atlantic mixed species stop seine/weir/pound 2010-2014
net (except the NC roe mullet stop net)
----------------------------------------------------------------------------------------------------------------
Virginia pound net 2010-2014
----------------------------------------------------------------------------------------------------------------
Classification
The Chief Counsel for Regulation of the Department of Commerce
certified to the Chief Counsel for Advocacy of the Small Business
Administration that this rule would not have a significant economic
impact on a substantial number of small entities. The factual basis
leading to the certification is set forth below.
NMFS has estimated that approximately 65,940 vessels participating
in 19 fisheries listed in
[[Page 27658]]
Table 1 would be eligible to carry an observer if requested. However,
NMFS would only request a fraction of the total number of participants
to carry an observer based on the sampling protocol identified for each
fishery by regional observer programs. As noted throughout this
proposed rule, NMFS would select vessels and focus coverage in times
and areas where fishing effort overlaps with sea turtle distribution.
Due to the unpredictability of fishing effort, NMFS cannot determine
the specific number of vessels that would be requested to carry an
observer.
If a vessel is requested to carry an observer, fishers will not
incur any direct economic costs associated with carrying that observer.
Potential indirect costs to individual fishers required to take
observers may include: lost space on deck for catch, lost bunk space,
and lost fishing time due to time needed to process bycatch data. For
effective monitoring, however, observers will rotate among a limited
number of vessels in a fishery at any given time and each vessel within
an observed fishery has an equal probability of being requested to
accommodate an observer. The potential indirect costs to individual
fishers are expected to be minimal because observer coverage would only
be required for a small percentage of an individual vessel's total
annual fishing time. In addition, 50 CFR 222.404(b) states that an
observer will not be placed on a vessel if the facilities for
quartering an observer or performing observer functions are inadequate
or unsafe, thereby exempting vessels too small to accommodate an
observer from this requirement. As a result of this certification, an
initial regulatory flexibility analysis is not required and was not
prepared.
The requirements to carry an observer when requested for those
fisheries included on the 2010 AD through this final rule are included
under an existing collection-of-information that was approved by the
Office of Management and Budget (OMB) under OMB control number 0648-
0593.
Notwithstanding any other provision of the law, no person is
required to respond to, nor shall any person be subject to a penalty
for failure to comply with, a collection of information subject to the
requirements of the Paperwork Reduction Act, unless that collection of
information displays a currently valid OMB Control Number.
This final rule has been determined to be not significant for the
purposes of Executive Order 12866.
An environmental assessment (EA) was prepared under the National
Environmental Policy Act (NEPA) for regulations to implement this
observer requirement in 50 CFR part 222, subpart D. The EA concluded
that implementing these regulations would not have a significant impact
on the human environment. This fianl rule would not make any
significant change in the management of fisheries included on the AD,
and therefore, this final rule would not change the analysis or
conclusion of the EA. If NMFS takes a management action, for example,
requiring fishing gear modifications such as TEDs, NMFS would first
prepare an environmental document as required under NEPA and specific
to that action.
This final rule would not affect species listed as threatened or
endangered under the Endangered Species Act (ESA) or their associated
critical habitat. The impacts of numerous fisheries have been analyzed
in various biological opinions, and this final rule would not affect
the conclusions of those opinions. Including fisheries on the AD is not
considered to be a management action that would adversely affect
threatened or endangered species. If NMFS takes a management action,
for example, requiring modifications to fishing gear and/or practices,
NMFS would review the action for potential adverse affects to listed
species under the ESA.
This final rule would have no adverse impacts on sea turtles and
may have a positive impact on sea turtles by improving knowledge of sea
turtles and the fisheries interacting with sea turtles through
information collected from observer programs.
Literature Cited