Taking of Marine Mammals Incidental to Commercial Fishing Operations; Atlantic Large Whale Take Reduction Plan Regulations, 57104-57194 [07-4904]
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57104
Federal Register / Vol. 72, No. 193 / Friday, October 5, 2007 / Rules and Regulations
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Parts 229, 635, and 648
[Docket No. 0612242977–7216–01; I.D.
120304D]
RIN 0648–AS01
Taking of Marine Mammals Incidental
to Commercial Fishing Operations;
Atlantic Large Whale Take Reduction
Plan Regulations
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
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AGENCY:
SUMMARY: NMFS issues this final rule to
amend the regulations implementing the
Atlantic Large Whale Take Reduction
Plan (ALWTRP). This final rule revises
the management measures for reducing
the incidental mortality and serious
injury to the Northern right whale
(Eubalaena glacialis), humpback whale
(Megaptera novaeangliae), and fin
whale (Balaenoptera physalus) in
commercial fisheries to meet the goals
of the Marine Mammal Protection Act
(MMPA) and the Endangered Species
Act (ESA). The measures identified in
the ALWTRP are also intended to
benefit minke whales (Balaenoptera
acutorostrata), which are not strategic,
but are known to be taken incidentally
in commercial fisheries. This final rule
implements additional regulations for
the fisheries currently covered by the
ALWTRP (the Northeast sink gillnet,
Northeast/Mid-Atlantic American
lobster trap/pot, Mid-Atlantic gillnet,
Southeast Atlantic gillnet, and
Southeastern U.S. Atlantic shark gillnet
fisheries) and regulates several fisheries
from the MMPA List of Fisheries for the
first time under the ALWTRP, including
the following: Northeast anchored float
gillnet, Northeast drift gillnet, Atlantic
blue crab, and Atlantic mixed species
trap/pot fisheries targeting crab (red,
Jonah, and rock), hagfish, finfish (black
sea bass, scup, tautog, cod, haddock,
pollock, redfish (ocean perch), and
white hake), conch/whelk, and shrimp.
DATES: The amendments to §§ 229.2,
229.3, and 648.264(a)(6)(i) are effective
April 5, 2008 and the amendment to
§ 635.69(a)(3) is effective November 5,
2007.
As specified in the regulatory text
section of this document, amendments
to § 229.32 are effective as follows:
• Paragraphs (f) introductory text,
(f)(2), and (f)(3) are revised effective
November 5, 2007;
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• Amendments to § 229.32(f)(1)(iii)
and (g)(4)(i)(B)(1)(vi) are added effective
November 5, 2007 to April 5, 2008;
• Paragraphs (f)(1)(ii) and
(g)(4)(i)(B)(1)(iii) are removed and
reserved effective November 5, 2007;
• Subsequent revision of § 229.32 is
effective April 5, 2008 except for
paragraphs (c)(5)(ii)(B), (c)(6)(ii)(B),
(c)(7)(ii)(C), (c)(8)(ii)(B), (c)(9)(ii)(B),
(d)(6)(ii)(D), and (d)(7)(ii)(D), which will
be effective October 5, 2008.
ADDRESSES: Copies of the Final
Environmental Impact Statement/
Regulatory Impact Review for this
action can be obtained from the
ALWTRP Web site listed under the
Electronic Access portion of this
document. Atlantic Large Whale Take
Reduction Team (ALWTRT) meeting
summaries, progress reports on
implementation of the ALWTRP, and
the small entity compliance guide may
be obtained by writing Diane Borggaard,
NMFS, Northeast Region, 1 Blackburn
Drive, Gloucester, MA 01930. For
additional ADDRESSES and Web sites for
document availability see
SUPPLEMENTARY INFORMATION section.
Written comments regarding the
burden-hour estimates or other aspects
of the collection-of-information
requirements contained in this final rule
may be submitted to Mary Colligan,
Assistant Regional Administrator for
Protected Resources, National Marine
Fisheries Service, Northeast Region, 1
Blackburn Drive, Gloucester, MA 01930
and by e-mail to
David_Rostker@omb.eop.gov, or fax to
202–395–7285.
FOR FURTHER INFORMATION CONTACT:
Diane Borggaard, NMFS, Northeast
Region, 978–281–9300 Ext. 6503,
diane.borggaard@noaa.gov; Kristy Long,
NMFS, Office of Protected Resources,
301–713–2322, kristy.long@noaa.gov; or
Barb Zoodsma, NMFS, Southeast
Region, 904–321–2806,
barb.zoodsma@noaa.gov.
SUPPLEMENTARY INFORMATION:
Electronic Access
Several of the background documents
for the ALWTRP and the take reduction
planning process can be downloaded
from the ALWTRP Web site at https://
www.nero.noaa.gov/whaletrp/. Copies
of the most recent marine mammal stock
assessment reports may be obtained by
writing to Dr. Richard Merrick, NMFS,
166 Water Street, Woods Hole, MA
02543 or can be downloaded from the
Internet at https://www.nefsc.noaa.gov/
psb/assesspdfs.htm. The complete text
of the regulations implementing the
ALWTRP can be found either in the
Code of Federal Regulations (CFR) at 50
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CFR 229.32 or downloaded from the
Web site, along with a guide to the
regulations.
Background
This final rule implements
modifications to the ALWTRP as
suggested by the ALWTRT, as well as
modifications deemed necessary by
NMFS to meet the goals of the MMPA
and ESA. Details concerning the
development and justification of this
final rule were provided in the preamble
to the proposed rule (70 FR 35894, June
21, 2005) and are not repeated here.
This final rule also incorporates a recent
amendment to the ALWTRP (72 FR
34632, June 25, 2007) that implemented,
with revisions, previous ALWTRP
regulations by expanding the Southeast
U.S. Restricted Area to include waters
within 35 nm (64.82 km) of the South
Carolina coast, dividing the Southeast
U.S. Restricted Area into Southeast U.S.
Restricted Areas North and South, and
modified regulations pertaining to
gillnetting within the Southeast U.S.
Restricted Area.
Changes to the Boundaries and Seasons
The ALWTRP gear modifications for
regulated areas of the east coast will
extend out to the eastern edge of the
exclusive economic zone (EEZ)
(effective April 7, 2008) (See Figures 1
and 2). The ALWTRP will also modify
seasonal requirements along the east
coast (effective April 7, 2008). Broadbased gear modifications will be
required on a year-round basis from
Maine to 41°18.2′ N. lat. and 71°51.5′ W.
long. (Watch Hill, RI), south to 40°00′ N.
lat., and east to the eastern edge of the
EEZ. NMFS will require gear
modifications in the Mid and South
Atlantic (called ‘‘Mid/South Atlantic’’
from this point) on a seasonal basis,
from September 1 to May 31, when
more sightings are reported and the risk
of entanglement with commercial
fishing gear is greater. Under this final
rule, a line drawn from 41°18.2′ N. lat.
and 71°51.5′ W. long. (Watch Hill, RI),
south to 40°00′ N. lat., and east to the
eastern edge of the EEZ, will serve as
the northern boundary for seasonal gear
modifications in the Mid/South Atlantic
and 32°00′ N. lat. (near Savannah, GA)
east to the eastern edge of the EEZ will
serve as the southern boundary.
Portions of the Mid/South Atlantic
Gillnet Waters (i.e., waters within 35 nm
(64.82 km) of the South Carolina coast)
will be included in the Southeast U.S.
Restricted Area (a gillnet management
area) during the restricted periods
associated with the right whale calving
season (i.e. November 15 to April 15).
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NMFS is revising the seasons and
boundaries for the southeast from
November 15 to April 15 for all
ALWTRP regulated fisheries, except for
the gillnet fisheries modified through
the recent amendment to the ALWTRP
(72 FR 34632, June 25, 2007), between
32°00′ N. lat. (near Savannah, GA) and
29°00′ N. lat. (near New Smyrna Beach,
FL) east to the eastern edge of the EEZ.
From December 1 to March 31,
restrictions will be required for the
Atlantic blue crab and Atlantic mixed
species trap/pot fisheries and the
Southeast Atlantic gillnet fishery
between 29°00′ N. lat. and 27°51′ N. lat.
(near Sebastian Inlet, FL) east to the
eastern edge of the EEZ, and for the
Southeastern U.S. Atlantic shark gillnet
fishery between 29°00′ N. lat. and
26°46.50′ N. lat. (near West Palm Beach,
FL) east to the eastern edge of the EEZ.
The Southeastern U.S. shark gillnet
fishery as regulated in this final rule
includes shark gillnetting with 5-inch
(12.7-cm) or greater stretched mesh
south of the South Carolina/Georgia
border.
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Changes to the Lobster Trap/Pot Gear
Requirements
Northern Inshore State and Nearshore
Trap/Pot Waters, Cape Cod Bay
Restricted Area (May 16–December 31),
Stellwagen Bank/Jeffreys Ledge
Restricted Area, and Great South
Channel Restricted Area (Nearshore
Portion)
The regulations for Northern
Nearshore Trap/Pot Waters, Stellwagen
Bank/Jeffreys Ledge Restricted Area,
and the Federal portion of the Cape Cod
Bay Restricted Area (May 16–December
31) will continue to require one buoy
line on trawls of 5 or fewer traps.
For Northern Inshore State Trap/Pot
Waters and the state portion of the Cape
Cod Bay Restricted Area (May 16–
December 31), this final rule will
eliminate the Lobster Take Reduction
Technology List (i.e., a list of gear
modification options) and require a 600lb (272.2-kg) weak link on all flotation
devices and/or weighted devices (except
traps/pots, anchors, and leadline woven
into the buoy line) attached to the buoy
line (effective April 7, 2008).
This final rule will also lower the
weak link breaking strength on all
flotation devices and/or weighted
devices attached to the buoy line in the
nearshore portion of the Great South
Channel Restricted Area that overlaps
with Lobster Management Area (LMA) 2
and the Outer Cape (July 1–March 31)
from 2,000 lb (907.2 kg) to 600 lb (272.2
kg) (effective April 7, 2008). All
fishermen in the nearshore portion of
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15:40 Oct 04, 2007
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the Great South Channel Restricted Area
will then be required to have a 600-lb
(272.2-kg) weak link on all flotation
devices and/or weighted devices (except
traps/pots, anchors, and leadline woven
into the buoy line) attached to the buoy
line.
Offshore Trap/Pot Waters Area and
Great South Channel Restricted Area
(Offshore Portion)
This final rule will extend the
southern boundary of the Offshore Trap/
Pot Waters Area by following the 100fathom (600-ft or 182.9-m) line from
35°30′ N. lat. (just north of Cape
Hatteras, NC) to 27°51′ N. lat. and then
extending out to the eastern edge of the
EEZ (effective April 7, 2008). In
addition to the current requirements,
this final rule will lower the maximum
breaking strength of weak links and
require weak links with appropriate
breaking strength on all flotation
devices and/or weighted devices (except
traps/pots, anchors, and leadline woven
into the buoy line) attached to the buoy
line in Offshore Trap/Pot Waters that
overlaps with the LMA 3 (including the
area known as the Area 2/3 Overlap and
Area 3/5 Overlap) and the offshore
portion of the Great South Channel
Restricted Area that overlaps with the
LMA 2/3 overlap and LMA 3 Areas from
2,000 lb (907.2 kg) to 1,500 lb (680.4 kg)
(effective April 7, 2008).
Southern Nearshore Trap/Pot Waters
Area
This final rule will extend the
southern boundary of the Southern
Nearshore Trap/Pot Waters Area by
following the 100-fathom (600-ft or
182.9-m) line from 35°30′ N. lat. to
27°51′ N. lat. and then extending the
boundary inshore to the shoreline or
exempted areas. The Southern
Nearshore Trap/Pot Waters is defined by
LMAs 4, 5, and 6 (except for the
exempted areas) north of 35°30′ N. lat.
and by the 100-fathom (600-ft or 182.9m) line west to the shoreline or
exempted areas south of 35°30′ N. lat. In
addition to the current requirements,
this final rule will implement the
regulations currently required in the
Southern Nearshore Trap/Pot Waters in
the portion of LMA 6 that is neither
exempted under the ALWTRP waters
(i.e., mouth of Long Island Sound) nor
currently regulated by the ALWTRP
(effective April 7, 2008). This final rule
will also require a 600-lb (272.2-kg)
weak link on all flotation devices and/
or weighted devices (except traps/pots,
anchors, and leadline woven into the
buoy line) attached to the buoy line.
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Changes to the Other Trap/Pot Gear
Requirements
Effective April 7, 2008, NMFS will
regulate the following trap/pot fisheries
under the ALWTRP (designated as
‘‘Other Trap/Pot Fisheries’’): Crab (red,
Jonah, rock, and blue), hagfish, finfish
(black sea bass, scup, tautog, cod,
haddock, pollock, redfish (ocean perch),
and white hake), conch/whelk, and
shrimp. Through this final rule, these
Other Trap/Pot fisheries will be
required to comply with current
ALWTRP regulations, including the
universal gear modifications, and will
follow the same area designations and
requirements (e.g., weak links, Seasonal
Area Management (SAM) program
requirements as modified in this final
rule, and Cape Cod Bay and Great South
Channel Area restrictions) currently
required and revised for the lobster trap/
pot fisheries covered by the ALWTRP.
Where applicable, these fisheries will
also be regulated under the ALWTRP
within the portion of LMA 6 that is not
exempted by the ALWTRP (i.e., mouth
of Long Island Sound). In addition to
complying with the current ALWTRP
requirements, the Other Trap/Pot
Fisheries will be required to comply
with the modifications for the lobster
trap/pot fishery specified in this final
rule (effective April 7, 2008) except for
the groundline requirements where
applicable as noted under the ‘‘BroadBased Gear Modifications’’ section
below.
Red Crab Trap/Pot Gear
Through this final rule, the maximum
weak link breaking strength will be
lowered from 3,780 lb (1,714.6 kg) to
2,000 lb (907.2 kg). A 2,000-lb (907.2-kg)
weak link will be required on all
flotation devices and/or weighted
devices (except traps/pots, anchors, and
leadline woven into the buoy line)
attached to the buoy line in the red crab
fishery (effective April 7, 2008).
Changes to the All Trap/Pot Gear
Requirements
Broad-Based Gear Modifications
The majority of the broad-based gear
modifications identified in this final
rule for trap/pot gear will become
effective six months after publication of
this final rule, April 7, 2008, except for
the groundline requirement that will be
phased-in and effective October 6, 2008,
except in SAM and Cape Cod Bay
Restricted Areas. When the majority of
the broad-based gear modifications
become effective on April 7, 2008, the
Dynamic Area Management (DAM)
program will be eliminated. When the
sinking/neutrally buoyant groundline
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requirement becomes fully effective,
October 6, 2008, this final rule will
eliminate the Seasonal Area
Management (SAM) program. However,
until October 6, 2008, the Other Trap/
Pot Fisheries will be subject to SAM
program requirements (see
modifications to area and gear
requirements as noted in this final rule).
ALWTRP-Regulated Trap/Pot Waters
Due to the addition of new trap/pot
fisheries, ALWTRP-Regulated Lobster
Waters will be re-designated as
ALWTRP-Regulated Trap/Pot Waters to
reflect the broader application of
ALWTRP requirements. Accordingly,
under the final rule, the term ‘‘lobster
trap/pot’’ will be replaced with ‘‘trap/
pot’’ where it appears in the regulations
implementing the ALWTRP.
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Boundaries and Seasons
Under this final rule, the areas will be
created by establishing a line that is
bounded on the west by a line running
from 41°18.2′ N. lat. and 71°51.5′ W.
long. (Watch Hill, RI), south to 40°00′ N.
lat., and east to the eastern edge of the
EEZ. The gear fished in the area north
of this line will be required to
incorporate current and revised broadbased gear modifications year-round;
the gear fished in the area south of this
line to 32°00′ N. lat. and east to the
eastern edge of the EEZ will require gear
modifications from September 1 to May
31 (effective April 7, 2008). Areas south
of 32°00′ N. lat. will require gear
modifications in the following areas and
during the following seasonal time
periods: between the 32°00′ N. lat. and
29°00′ N. lat. east to the eastern edge of
the EEZ from November 15–April 15;
between 29°00′ N. lat. and 27°51′ N. lat.
east to the eastern edge of the EEZ from
December 1 through March 31 (effective
April 7, 2008).
Sinking/Neutrally Buoyant Groundlines
Under this final rule, the lobster trap/
pot fishery currently regulated by the
ALWTRP, as well as the other trap/pot
fisheries added through this final rule,
will be required to use groundline
composed entirely of sinking and/or
neutrally buoyant line in the applicable
areas and time periods effective twelve
months after publication of this final
rule (unless otherwise required in the
Cape Cod Bay Restricted Area for trap/
pots [January 1–May 15]). The sinking
and/or neutrally buoyant groundline
requirement will be effective in
expanded SAM areas effective 6 months
after publication of this final rule.
Based on public comments received
regarding the line between traps and
anchors, and a review of the groundline
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definition, NMFS finds that the
definition does not cover this portion of
the gear. (The groundline definition
‘‘with reference to trap/pot gear, means
a line connecting traps in a trap trawl,
and with reference to gillnet gear, means
a line connecting a gillnet or gillnet
bridle to an anchor or buoy line.’’)
NMFS did not specifically seek nor
receive public comment on the
groundline definition related to the line
between traps and anchors, and
accordingly cannot make any
adjustments to the definition at this
time. NMFS will be conducting further
investigations of this gear configuration
through contact with fishermen and
states to determine how common a
practice it is in trap/pot fisheries,
determine the type of line used in this
portion of the gear, quantify potential
risk if floating line is used, determine
any new issues that may be raised by
requiring sinking and/or neutrally
buoyant line in this area of the gear, and
discuss the appropriate management
response with the ALWTRT at the next
meeting.
Weak Links
Through this final rule, weak links of
the appropriate breaking strength will
be required on all flotation devices and/
or weighted devices (except traps/pots,
anchors, and leadline woven into the
buoy line) attached to the buoy line
(effective April 7, 2008) for all
ALWTRP-regulated areas and fisheries
during the time periods when ALWTRP
restrictions apply. The Other Trap/Pot
Fisheries added to the ALWTRP by this
final rule will also be subject to the
weak link requirements.
Changes to the Gillnet Gear
Requirements
Other Northeast Gillnet Waters,
Stellwagen Bank/Jeffreys Ledge
Restricted Area, Cape Cod Bay
Restricted Area (May 16–December 31),
Great South Channel Restricted Area
(July 1–March 31), and Great South
Channel Sliver Restricted Area
Anchored Gillnets
Under this final rule, NMFS will
require an 1,100-lb (499.0-kg) weak link
on all flotation devices and/or weighted
devices (except gillnets, anchors, and
leadline woven into the buoy line)
attached to the buoy line (effective April
7, 2008). For anchored gillnets in the
Northeast sink gillnet fishery, NMFS
will also require an increase in the
number of weak links per gillnet net
panel from one weak link with a
maximum breaking strength of 1,100 lb
(499.0 kg) to five or more weak links
with a maximum breaking strength of
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1,100 lb (499.0 kg), depending on the
length of the gillnet net panel (effective
April 7, 2008). The weak link
requirement will apply to all variations
in panel size. For example, gillnet net
panels of 50 fathoms (300 ft or 91.4 m)
or less in length, will be required to
have one weak link in the floatline at
the center of the gillnet net panel. For
gillnet net panels greater than 50
fathoms (300 ft or 91.4 m), weak links
will be placed continuously along the
floatline separated by a maximum
distance of 25 fathoms (150 ft or 45.7
m). For all variations in panel size, the
following weak link requirements will
apply: (1) Weak links will be placed in
the center of each of the up and down
lines at each end of each gillnet net
panel, and (2) one floatline weak link
will be placed as close as possible to
each end of the gillnet net panel just
before the floatline meets the up and
down line. Up and down line means the
line that connects the floatline and
leadline at the end of each gillnet net
panel.
In addition to the above configuration
for gillnet net panel weak links, NMFS
will allow the following option for all
variations in panel size: (1) Weak links
will be placed in the center of each of
the up and down lines at each end of
each gillnet net panel, (2) weak links
will be placed between the floatline tie
loops between gillnet net panels, and (3)
weak links will be placed between the
floatline tie loop and bridle or buoy line
at each end of a net string (depending
on how the gear is configured) (see
Figure 3). Tie loops mean the loops on
a gillnet net panel used to connect
gillnet net panels to the buoy line,
groundline, bridle, or each other. NMFS
will also be allowing the optional
configuration in the current SAM areas,
as well as in established DAM zones
when a gear modification option is
selected (effective November 5, 2007).
See the Changes from Proposed Rule
section (6) below for further information
on the rationale for this optional
configuration, as well as for allowing it
in the current SAM areas and
established DAM zones.
For the above configuration options,
weak links must be chosen from the
following combinations approved by
NMFS: Plastic weak links or rope of
appropriate breaking strength. If rope of
appropriate breaking strength is used
throughout the floatline or as the up and
down line, or if no up and down line
is present, then individual weak links
are not required on the floatline or up
and down line. In addition, all anchored
gillnets, regardless of the number of
gillnet net panels, will be required to be
securely anchored with the holding
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capacity equal to or greater than a 22lb (10.0-kg) Danforth-style anchor at
each end of the net string (effective
April 7, 2008). Dead weights and heavy
leadline will not be available as an
optional anchoring system. The same
configuration option would be required
for all gillnet net panels in a string.
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Mid/South Atlantic Gillnet Waters
Under this final rule, the Mid-Atlantic
Coastal Waters Area will be expanded
and renamed to include waters
currently unregulated by the ALWTRP
that include a component of the U.S.
Mid-Atlantic gillnet fishery and
Southeast Atlantic gillnet fishery.
Specifically, gillnet fisheries in the
waters from 72°30′ W. long., south to the
Virginia/North Carolina border, east to
the eastern edge of the EEZ, and
extending south to 32°00′ N. lat. and out
to the eastern edge of the EEZ will be
referred to as Mid/South Atlantic
Gillnet Waters (effective April 7, 2008).
Portions of the Mid/South Atlantic
Gillnet Waters (i.e., waters within 35 nm
(64.82 km) of the South Carolina coast)
are also included in the Southeast U.S.
Restricted Area during the November 15
to April 15 right whale calving season.
Anchored Gillnets
Under this final rule, all anchored
gillnets in the Mid/South Atlantic
Gillnet Waters must have an 1,100-lb
(499.0-kg) weak link on all flotation
devices and/or weighted devices (except
gillnets, anchors, and leadline woven
into the buoy line) attached to the buoy
line (effective April 7, 2008).
Additionally, if gillnets are not returned
to port with the vessel they must
contain five or more weak links
depending on the length of the gillnet
net panel, with a maximum breaking
strength no greater than 1,100 lb (499.0
kg) for each gillnet net panel; and be
anchored at each end with an anchor
capable of the holding capacity equal to
or greater than a 22-lb (10.0-kg)
Danforth-style anchor (effective April 7,
2008). The configuration options for
gillnet net panel weak links and
anchoring are similar to that specified
for anchored gillnets in the Other
Northeast Gillnet Waters section of this
rule. The same configuration option
would be required for all gillnet net
panels in a string. All gillnets, even if
returned to port with the vessel, must
also contain one weak link with a
maximum breaking strength no greater
than 1,100 lb (499.0 kg) in the center of
the floatline of each gillnet net panel up
to and including 50 fathoms (300 ft or
91.4 m) in length, or at least every 25
fathoms (150 ft or 45.7 m) along the
floatline for longer panels in previously
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unregulated waters (effective April 7,
2008).
Gillnets within 300 yards (900 ft or
274.3 m) of the shoreline of North
Carolina that are not returned to port
with the vessel will have an additional
option for setting their gear. Gillnets set
in this area may configure their gear as
follows: five or more weak links per
gillnet net panel (depending on the
length of the gillnet net panel) with a
maximum breaking strength of 600 lb
(272.2 kg) must be deployed, and be
anchored with the holding capacity
equal to or greater than an 8-lb (3.6-kg)
Danforth-style anchor on the offshore
end of the net string and with a dead
weight equal to or greater than 31-lb
(14.1-kg) on the inshore end of the net
string (effective April 7, 2008). The
entire net string must be set within 300
yards (900 ft or 274.3 m) of the beach
in North Carolina for this optional
anchoring system and gillnet net panel
weak link configuration. This
configuration is in addition to the final
configuration of five or more weak links
per gillnet net panel (depending on the
length of the gillnet net panel) with a
maximum breaking strength of 1,100-lb
(499.0-kg), and anchored with the
holding capacity equal to or greater than
a 22-lb (10.0-kg) Danforth-style anchor
on each end of the net string. Specifics
on the configuration options for the
placement of gillnet net panel weak
links can be found in the Other
Northeast Gillnet Waters section of this
rule.
At this time, NMFS is not regulating
gillnets that are anchored to the beach
and subsequently hauled onto the beach
to retrieve the catch. This fishing
technique is known to occur on the
beaches of North Carolina. NMFS will
be discussing the appropriate
management measures for this unique
fishery with the ALWTRT at a future
meeting. In the meantime, NMFS will be
conducting outreach and research on
this fishery to support future
discussions with the ALWTRT. NMFS
will be coordinating with the North
Carolina Department of Marine
Fisheries to revise the definition for
beach -based gear to help ensure
landings are reported accurately for
beach-based gear versus gillnets, among
other issues.
Drift Gillnets
Under this final rule, current
requirements for drift gillnet gear in
Mid/South Atlantic Gillnet Waters are
expanded in time and space as noted in
the Boundaries and Seasons section
above (effective April 7, 2008).
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57107
Other Southeast Gillnet Waters
Under this final rule, the management
area for the Southeast Atlantic gillnet
and Southeastern U.S. Atlantic shark
gillnet fisheries off Georgia and Florida
will be expanded and renamed
(effective April 7, 2008). Specifically,
this final rule will define the waters east
of 80°00′ W. long. from 32°00′ N. lat.
south to 26°46.5′ N. lat. and out to the
eastern edge of the EEZ as one ALWTRP
management area named ‘‘Other
Southeast Gillnet Waters’’. The
expansion of this area east to the eastern
edge of the EEZ will be consistent with
the ALWTRP area boundary expansion
in the Mid-Atlantic.
Under this final rule, NMFS will
establish the seasonal restricted time
period in Other Southeast Gillnet
Waters (effective April 7, 2008).
ALWTRP regulations for the Southeast
Atlantic gillnet fishery operating in the
Other Southeast Gillnet Waters between
32°00′ N. lat. to 29°00′ N. lat. (near New
Smyrna Beach, FL) will be effective
from November 15 to April 15, and
between 29°00′ N. lat. and 27°51′ N. lat.
will be effective from December 1 to
March 31. For the Southeastern U.S.
Atlantic shark gillnet fishery, ALWTRP
regulations in the Other Southeast
Gillnet Waters between 32°00′ N. lat. to
29°00′ N. lat. will be effective from
November 15 to April 15, and between
29°00′ N. lat. and 26°46.5′ N. lat. will be
effective from December 1 to March 31.
Southeast Atlantic Gillnet Fishery
All gillnet gear in Other Southeast
Gillnet Waters will be regulated in the
same manner as the Mid/South Atlantic
anchored gillnet fishery (effective April
7, 2008). The regulated waters for the
Southeast Atlantic gillnet fishery south
of 32°00′ N. lat. to 27°51′ N. lat. and east
from 80°00′ W. long. to the eastern edge
of the EEZ will be required to comply
with the ALWTRP universal gear
requirements (e.g., no buoy line floating
at the surface and no wet storage of
gear), as well as the following: gillnets
must have all flotation devices and/or
weighted devices (except gillnets,
anchors, and leadline woven into the
buoy line) attached to the buoy line
with a weak link having a maximum
breaking strength no greater than 1,100
lb (499.0 kg); and have all gillnet net
panels containing weak links with a
maximum breaking strength no greater
than 1,100 lb (499.0 kg) in the center of
each floatline of each 50 fathom (300 ft
or 91.4m) gillnet net panel or every 25
fathoms (150 ft or 45.7 m) for longer
panels (effective April 7, 2008).
In addition, under this final rule, all
gillnets in the Other Southeast Gillnet
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Waters that are not returned to port with
the vessel will be required to contain
five or more weak links, depending on
the length of the gillnet net panel, with
a maximum breaking strength no greater
than 1,100 lb (499.0 kg) for each gillnet
net panel; and be anchored at each end
with an anchor with the holding
capacity equal to or greater than a 22lb (10.0-kg) Danforth-style anchor
(effective April 7, 2008). The
configuration options for gillnet net
panel weak links and anchoring are
similar to that specified for anchored
gillnets in the Other Northeast Gillnet
Waters section of this final rule. The
same configuration option would be
required for all gillnet net panels in a
string.
yshivers on PROD1PC62 with RULES2
Southeastern U.S. Atlantic Shark
Gillnet Fishery
For the Southeastern U.S. Atlantic
Shark gillnet fishery operating in Other
Southeast Gillnet Waters, the following
requirements will be in effect: (1) No net
is set within 3 nautical miles (5.6 km)
of a right, humpback, or fin whale; and
(2) If a right, humpback, or fin whale
moves within 3 nautical miles (5.6 km)
of the set gear, the gear is removed
immediately from the water (effective
April 7, 2008).
Southeast U.S. Restricted Area (N and
S) and Southeast U.S. Monitoring Area
Under this final rule, the management
areas for the Southeastern U.S. Atlantic
shark gillnet and Southeast Atlantic
gillnet fishery management areas will be
redefined (effective April 7, 2008).
Specifically, for the Southeastern U.S.
Atlantic shark gillnet fishery, the
regulated waters landward of 80°00′ W.
long. from 27°51′ N. lat. to 26°46.5′ N.
lat. will be designated as the Southeast
U.S. Monitoring Area (rather than the
Southeast U.S. Observer Area). For both
the Southeastern U.S. Atlantic shark
gillnet and Southeast Atlantic gillnet
fisheries, the regulated waters landward
of 80°00′ W. long. from 32°00′ N. lat. to
27°51′ N. lat. will be designated as the
Southeast U.S. Restricted Area,
consisting of a northern area ‘‘N’’
between 32°00′ N. lat. and 29°00′ N. lat.
and a southern area ‘‘S’’ between 29°00′
N. lat. and 27°51′ N. lat.
Under this final rule, the management
areas for gillnet fisheries will be
regulated with rolling restrictions
(effective April 7, 2008). The
Southeastern U.S. Atlantic shark gillnet
and Southeast Atlantic gillnet fisheries
will be regulated in waters from 32°00′
N. lat. to 29°00′ N. lat. (near New
Smyrna Beach, FL) from November 15
through April 15. The Southeastern U.S.
Atlantic shark gillnet fishery will be
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regulated in waters from 29°00′ N. lat.
to 26°46.5′ N. from December 1 through
March 31, and the Southeast Atlantic
gillnet fishery will be regulated in
waters from 29°00′ N. lat. to 27°51′ N.
lat. from December 1 through March 31.
NMFS is also allowing the use of
vessel monitoring system (VMS) in lieu
of the 100-percent observer coverage
requirement for the Southeastern U.S.
Atlantic shark gillnets in the newly
defined Southeast U.S. Monitoring Area
(27°51′ N. lat. to 26°46.5′ N.) under the
ALWTRP (effective November 5, 2007).
Although 100-percent observer coverage
will no longer be required in this area,
NMFS will retain observer coverage
sufficient to produce statistically
reliable results for evaluating the impact
of the fishery on protected resources. In
light of the revised change from 100percent observer coverage to VMS,
NMFS is changing the name of the
‘‘Southeast U.S. Observer Area’’ to the
‘‘Southeast U.S. Monitoring Area.’’
Amendment 1 to the FMP for Atlantic
Tunas, Swordfish, and Sharks (68 FR
74746, December 24, 2003; 69 FR 19979,
April 15, 2004; and 69 FR 28106, May
18, 2004) requires gillnet vessels issued
directed shark limited access permits
that have gillnet gear on board,
regardless of their location, to employ a
NMFS approved VMS during the right
whale calving season specified in the
ALWTRP regulations. Currently, as
stated in the August 17, 2004, final rule
(69 FR 51010, August 17, 2004)
specifying November 15, 2004, as the
effective date of this requirement, the
applicable right whale calving season is
identified as November 15 through
March 31. This final rule will change
the right whale season specified in those
regulations for the Southeast U.S.
Monitoring Area to December 1 through
March 31 and amend the regulatory text
in 50 CFR 635.69(a)(3) regarding the
Highly Migratory Species (HMS) VMS
requirement for Southeastern U.S.
Atlantic shark gillnet vessels.
Changes to the Other Gillnet Gear
Requirements
Northeast Anchored Float Gillnet
Fishery
This final rule will regulate the
Northeast anchored float gillnet fishery
(gillnets anchored to the ocean floor
with lines running from the anchors to
the nets at the surface) according to the
requirements for the Northeast anchored
gillnet fishery requirements (effective
April 7, 2008). The Northeast anchored
float gillnet fishery will be subject to the
SAM program as modified in this final
rule until twelve months after
publication of this final rule, and to
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seasonal closures in right whale
restricted areas. Specifically, fishermen
using Northeast anchored float gillnets
will be prohibited from fishing inside
the Cape Cod Bay Restricted Area
annually from January 1 through May
15, and inside the Great South Channel
Restricted Area annually from April 1
through June 30.
Northeast Drift Gillnet Fishery
This final rule will regulate the
Northeast drift gillnet fishery (i.e., nets
that are present at the ocean surface and
are not anchored to the ocean floor on
either end) according to the
requirements for the Mid-Atlantic drift
gillnet fishery (effective April 7, 2008).
The Northeast drift gillnet fishery will
not be subject to the SAM program, but
drift gillnets will be prohibited from
Cape Cod Bay Restricted Area from
January 1 through May 15 and from the
Great South Channel Restricted Area
from April 1 through June 30 (similar to
the requirements for anchored gillnet),
except for the Sliver Area, where
restricted drift gillnet fishing will be
allowed.
Changes to the All Gillnet Gear
Requirements
Broad-Based Gear Modifications
Most of the broad-based gear
modifications for gillnet gear identified
in this final rule will become effective
six months after publication of this final
rule, April 7, 2008, except for the
groundline requirement discussed
below, which will be phased-in and
effective twelve months after
publication of this final rule (except in
SAM areas), October 6, 2008. When the
majority of the broad-based gear
modifications become effective on April
7, 2008, the DAM program will be
eliminated. When the sinking/neutrally
buoyant groundline requirement
becomes fully effective, October 6, 2008,
this final rule will eliminate the SAM
program. However, until this occurs,
some of the other gillnet fisheries that
will be added to the ALWTRP will be
subject to the SAM program (see
modifications to area and gear
requirements as noted in this final rule).
Boundaries and Seasons
Under this final rule, an area bounded
on the west by a line running from
41°18.2′ N. lat. and 71°51.5′ W. long.
(Watch Hill, RI), south to 40°00′ N. lat.,
and east to the eastern edge of the EEZ
will be created. The gillnet gear fished
in the area north of this line will be
required to incorporate current and
revised broad-based gear modifications
year-round. Gillnet gear fished in the
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area south of this line to 32°00′ N. lat.
and east to the eastern edge of the EEZ
will be required to comply with the
broad-based gear modifications detailed
above in Mid/South Atlantic Gillnet
Waters from September 1 to May 31.
However, portions of the Mid/South
Atlantic Gillnet Waters (i.e., waters
within 35 nm (64.82 km) of the South
Carolina coast) will be included in the
Southeast U.S. Restricted Area during
the November 15 to April 15 right whale
calving season. Gillnet fishing in the
area south of 32°00′ N. lat. will be
required to comply with the broadbased gear modifications in the
following areas and seasonal time
periods: All gillnet fisheries (Southeast
Atlantic and Southeastern U.S. Atlantic
shark) between 32°00′ N. lat. and 29°00′
N. lat. from November 15–April 15;
Southeast Atlantic gillnet fishery
between 29°00′ N. lat. and 27°51′ N. lat.
east to the eastern edge of the EEZ from
December 1–March 31; and
Southeastern U.S. Atlantic shark gillnet
fisheries between 29°00′ N. lat. and
26°46.5′ N. lat. east to the eastern edge
of the EEZ from December 1–March 31.
ALWTRP, and the Northeast anchored
float gillnet fishery, which will be
added by this final rule, will be required
to use groundline composed entirely of
sinking and/or neutrally buoyant line in
the areas and time periods covered
under the ALWTRP effective on October
6, 2008. The sinking and/or neutrally
buoyant groundline requirement will be
effective in expanded SAM areas
effective on April 7, 2008.
Sinking/Neutrally Buoyant Groundlines
Revised SAM Program
The final rule will amend the SAM
program by establishing new boundaries
for the SAM areas and revising the gear
modifications required for fishing
Under this final rule, the Northeast
anchored gillnet, Mid-Atlantic anchored
gillnet, and Southeast Atlantic gillnet
fisheries currently regulated by the
Weak Links
Under this final rule, to further reduce
the risk of serious injury and mortality
from entanglement in gillnet gear, weak
links having a maximum breaking
strength of 1,100 lb (499.0 kg) will be
required on all flotation devices and/or
weighted devices (except gillnets,
anchors, and leadline woven into the
buoy line) attached to the buoy line
(effective April 7, 2008). This
requirement will apply to all current
and revised ALWTRP regulated areas
and gillnet fisheries. The weak link
requirement is intended to reduce the
risk of entanglement and serious injury
or mortality due to entanglements in
buoy lines and surface systems.
57109
within these areas. The changes to the
SAM program described in this final
rule will become effective on April 7,
2008, to protect right whales. The SAM
program will be eliminated October 6,
2008, when all of the broad-based gear
modifications are effective.
This final rule will modify the
existing coordinates for the SAM areas.
Specifically, the western boundary of
SAM West will be extended westward
to encompass seasonal aggregations of
right whales that occur north of the
Cape Cod Bay Restricted Area.
Similarly, the southern boundary of
SAM West will be extended further
south, adjoining the Great South
Channel Restricted Sliver Area, to
encompass seasonal aggregations of
right whales that occur south of the
current SAM West and west of the Great
South Channel Restricted Area. Finally,
the southern boundary of SAM East
would be revised to include the Great
South Channel Restricted Area
including the Sliver Area, but will
exclude the southeast corner of the
existing SAM East area where there
have been very few right whale
sightings. The western boundary of
SAM East will be extended west to 69°
45′W. long. to encompass right whales
that might remain in SAM West in May
(after the SAM West area restrictions
have expired) (Table 1; Figure 8).
TABLE 1.—SEASONAL AREA MANAGEMENT
Point
Latitude (North)
Longitude (West)
SAM West Polygon—in Effect From March 1–April 30
1W
2W
3W
4W
5W
6W
7W
8W
1W
........................................
........................................
........................................
........................................
........................................
........................................
........................................
........................................
........................................
42°30′ ..............................................................................
42°30′ ..............................................................................
41°48.9′ ...........................................................................
41°40′ ..............................................................................
41°40′ ..............................................................................
42°04.8′ ...........................................................................
42°12′ ..............................................................................
42°12′ ..............................................................................
42°30′ ..............................................................................
70°30′ (NW Corner)
69°24′
69°24′
69°45′
69°57′ along the eastern shoreline of Cape Cod to
70°10′
70°15′
70°30′
70°30′ (NW Corner)
SAM East Polygon—in Effect From May 1–July 31
1E
2E
3E
4E
5E
1E
.........................................
.........................................
.........................................
.........................................
.........................................
.........................................
42°30′
42°30′
42°09′
41°00′
41°40′
42°30′
..............................................................................
..............................................................................
..............................................................................
..............................................................................
..............................................................................
..............................................................................
yshivers on PROD1PC62 with RULES2
Revised SAM Gear Modifications
In addition to the changes discussed
above, this final rule will revise the gear
modifications required for fishing
within the SAM areas during the
applicable time periods. Under this final
rule, NMFS will allow the use of two
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15:40 Oct 04, 2007
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69°45′ (NW Corner)
67°27′
67°08.4′
69°05′
69°45′
69°45′ (NW Corner)
buoy lines per trap/pot trawl or per net
string, allow the use of floating line on
the bottom one-third or less of the buoy
line, and allow two configuration
options for gillnet net panel weak links.
The same configuration option would be
required for all gillnet net panels in a
string.
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Changes to the SAM Program for All
Trap/Pot Gear
Under this final rule, in addition to
the measures revised for trap/pot
fisheries, the following requirements
specific to the SAM and DAM programs
would apply. The SAM areas will be
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expanded and all lobster trap/pot
fisheries operating within these areas
during the restricted time periods would
be subject to the current SAM
restrictions, plus the following: A
second buoy line will be allowed and
the bottom one-third of the buoy line
may consist of floating line. In addition,
the trap/pot fisheries subject to the SAM
program will be expanded to include:
hagfish, finfish (black sea bass, scup,
tautog, cod, haddock, pollock redfish,
and white hake), conch/whelk, shrimp,
red, blue, rock, and Jonah crab. The
expanded SAM area will include the
Great South Channel Restricted Area;
therefore, trap/pot gear will be subject to
the SAM program inside right whale
restricted areas during time periods
when the requirements for fishing
inside these areas are no more
conservative than the surrounding
waters (i.e., when the protections of
right whale restricted areas disappear).
However, the more restrictive Great
South Channel Restricted Trap/Pot Area
closure (April 1 through June 30) will
supercede the SAM program. As a
result, gear modifications for fishing
with trap/pot gear in the SAM area will
apply in the Great South Channel
Restricted Trap/Pot Area from July 1
through July 31. The DAM program will
be eliminated, and replaced with the
expanded SAM areas (effective April 7,
2008).
Changes to the SAM Program for Gillnet
Gear
Under this final rule, in addition to
the measures revised for gillnet
fisheries, the following requirements
specific to the SAM and DAM programs
would apply. The SAM areas will be
expanded, and all gillnet fisheries
operating within these areas during the
restricted time periods will be subject to
the current SAM restrictions, plus the
following: A second buoy line will be
allowed and the bottom one-third of the
buoy line may be composed of floating
line. In addition, gillnet fisheries would
be allowed two configuration options
for gillnet net panel weak links as noted
in the Other Northeast Gillnet Waters
section of this rule. The gillnet fisheries
regulated under the SAM program will
be expanded to include Northeast
anchored float gillnets. The expanded
SAM area will include the Great South
Channel Restricted Area; therefore,
gillnet gear will be subject to the SAM
program inside right whale restricted
areas during time periods when the
requirements for fishing inside these
areas are no more conservative than the
surrounding waters (i.e., when the
protections of right whale restricted
areas disappear). However, the more
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restrictive Great South Channel
Restricted Gillnet Area closure (April 1
through June 30) will supercede the
SAM program. As a result, gear
modifications for fishing with gillnet
gear in the SAM area will apply in the
Great South Channel Restricted Gillnet
Area from July 1 through July 31, and
in the Great South Channel Sliver
Restricted Area from May 1 through July
31. The DAM program will be
eliminated, and replaced with the
expanded SAM areas (effective April 7,
2008).
Other Changes for All Trap/Pot and
Gillnet Gear
DAM Program
The majority of the modifications in
this final rule will become effective on
April 7, 2008, including the
replacement of the DAM program.
Consequently, on April 7, 2008, when
the SAM areas are expanded, the
expanded SAM program will replace the
DAM program. However, until April 7,
2008, the currently regulated trap/pot
and gillnet fisheries, will be subject to
both the SAM and DAM programs. After
April 7, 2008, the currently regulated
trap/pot and gillnet fisheries, as well as
those added to the ALWTRP, will be
subject to the expanded SAM program.
Groundlines
Under this final rule, for both trap/pot
and gillnet fisheries, the SAM program
will be eliminated and replaced with
broad-based gear modifications,
including a requirement that all
groundlines must be composed of
sinking and/or neutrally buoyant line,
effective on October 6, 2008 (unless
otherwise required in the Cape Cod Bay
Restricted Area for trap/pot (January 1–
May 15) or SAM areas).
Gear Marking
Under this final rule, NMFS will
expand requirements to fisheries and
areas not previously regulated under the
ALWTRP or required to mark gear such
as the following: Northeast drift gillnet;
Northeast anchored float gillnet;
Northern Inshore State Trap/Pot Waters;
LMA 6 portion of Southern Nearshore
Trap/Pot Waters; Mid/South Atlantic
Gillnet Waters; and Other Southeast
Gillnet Waters (effective April 7, 2008).
The gear marking scheme will require
one 4-inch (10.2 cm) colored mark
midway along the buoy line.
Additionally, the gear marking scheme
will require all surface buoys to identify
the vessel registration number, vessel
documentation number, Federal permit
number, or whatever positive
identification marking is required by the
vessel’s home-port state (effective April
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Sfmt 4700
7, 2008). Under this final rule, the color
and marking scheme for nets used in the
Southeastern U.S. Atlantic shark gillnet
fishery will remain status quo and only
buoy lines greater than 4 feet (1.2 m) in
length would need to be marked for this
fishery.
Trap/Pot Gear Marking Colors
The ALWTRP will require fishermen
to mark their trap/pot buoy lines with
one red 4-inch (10.2 cm) mark while
they fish in the following management
areas: Cape Cod Bay Restricted Area,
Northern Nearshore Trap/Pot Waters,
and Stellwagen Bank/Jeffreys Ledge. To
remain consistent with the gear marking
color scheme in the North Atlantic,
under this final rule, NMFS will require
red marking on the buoy lines of trap/
pot gear fished in Northern Inshore
State Trap/Pot Waters. The trap/pot gear
marking color in the Great South
Channel Restricted Area is black.
However, under this final rule, for
consistency with nearby management
areas, the Great South Channel
Restricted Area gear marking color will
be either black or red, depending on the
area of overlap with offshore (i.e., LMA
2/3 Overlap and LMA 3) and nearshore
areas (i.e., LMA 2 and the Outer Cape),
respectively. The gear marking colors
for trap/pot gear in the Southern
Nearshore Trap/Pot Waters and Offshore
Trap/Pot Waters will remain orange and
black, respectively.
Gillnet Gear Marking Colors
Under this final rule, for consistency
with the current gillnet gear marking
scheme in the Northeast Atlantic, NMFS
will require one 4-inch (10.2-cm) green
mark midway along the buoy line for
the two new fisheries that will be added
to the ALWTRP: Northeast drift gillnet
and Northeast anchored float gillnet.
Prior to this final rule, there were no
gear marking requirements for the two
gillnet fisheries operating in the Mid/
South Atlantic: the Mid/South Atlantic
anchored gillnet and Mid/South
Atlantic drift gillnet fisheries. Under
this final rule, NMFS will require that
these fisheries mark their buoy lines
with one 4-inch (10.2-cm) blue mark
midway along the buoy line.
Under this final rule, the Southeast
Atlantic gillnet fishery will be required
to mark their buoy lines with one 4-inch
(10.2-cm) yellow mark midway on the
buoy line in the same manner as the
Mid/South Atlantic gillnet fisheries. As
mentioned above, the color and marking
scheme for nets used in the
Southeastern U.S. Atlantic shark gillnet
fishery would remain status quo and
only buoy lines greater than 4 feet (1.2
m) in length will need to be marked.
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Exempted Waters
Modifications to the exempted waters
are effective on April 7, 2008.
yshivers on PROD1PC62 with RULES2
Coastal Exempted Waters
To be consistent throughout the east
coast, under this final rule, with the
exceptions detailed below, NMFS will
exempt all marine and tidal waters
landward of the 72 COLREGS
demarcation lines. The 72 COLREGS
lines are well known and widely
published lines of demarcation. In four
areas, Casco Bay (Maine), Portsmouth
Harbor (New Hampshire), the state of
Massachusetts, and Long Island Sound
and Gardiners Bay (New York), NMFS
will not use the 72 COLREGS lines and
will instead create different exemption
lines. Any exemption lines for these
areas, as well as areas where the 72
COLREGS lines do not exist, are
explained in the Changes From the
Proposed Rule sections (2) through (4)
below.
Based on the public comments
received and an analysis of the available
data, NMFS will use an exemption line
for the coast of Maine that is largely
based on the line suggested by the
Maine Department of Marine Resources
(Maine DMR). The final exemption line
for Maine will begin at the MaineCanada border and extend south and
west along the Maine coastline to
Odiornes Point, New Hampshire. The
line will be connected using a series of
25 buoys and islands along the Maine
coast (Figure 4). See the regulations in
this final rule for the coordinates of the
Maine exemption line. See Changes
From the Proposed Rule section (2)
below for further information on the
rationale for the final Maine exemption
line.
Through this final rule, NMFS is
modifying the exempted waters for New
Hampshire’s three harbors, two as
proposed and one slightly modified. As
proposed, NMFS will exempt Rye and
Hampton Harbors according to the lines
drawn across the headlands which mark
their entrances to the sea. Portsmouth
Harbor will not be exempted according
to the 72 COLREGS demarcation line
(the only 72 COLREGS line found in the
state) because it will be exempted
through the final exemption line for
Maine, as this line’s final coordinate is
located at Odiornes Point, New
Hampshire.
The exempted waters for
Massachusetts will continue to include
state waters landward of the first bridge
over any embayment, harbor, or inlet.
See the Changes From the Proposed
Rule section (3) below for further
information on the rationale for the final
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15:40 Oct 04, 2007
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Massachusetts exemption line. This
final rule will not modify the current
exemption lines for Massachusetts or
Rhode Island, except for minor
refinement of the exemption line
coordinates for Point Judith Pond and
Quonochontaug Pond Inlets in Rhode
Island. However, under this final rule,
NMFS will clarify that the exemption
line coordinates drawn for Narragansett
Bay and the Sakonnet River match the
72 COLREGS lines for these waters
(Figure 5).
In New York, with the exception of
New York Harbor, all embayments,
harbors, and inlets are currently
exempted under the ALWTRP. Under
this final rule, these exempted waters
will remain unchanged with the
exception of the Long Island Sound and
Gardiners Bay area. However, NMFS
will clarify that the exemption lines for
Shinnecock Bay Inlet, Moriches Bay
Inlet, Fire Island Inlet, and Jones Inlet
match the 72 COLREGS demarcation
lines. In addition, NMFS will create an
exemption line for New York Harbor
based on the 72 COLREGS line. This is
a line drawn from East Rockaway Inlet
Breakwater Light to Sandy Hook Light.
Under this final rule, NMFS will exempt
a portion of Block Island Sound
landward of the territorial sea baseline
which extends from Watch Hill Point,
Rhode Island, to Montauk Point, New
York (Figure 5). See the Changes From
the Proposed Rule section (4) below for
further information on the rationale for
creating the Block Island Sound
exemption line.
NMFS clarifies that the entire
shoreline of New Jersey would be
exempted landward of the 72 COLREGS
demarcation lines. In doing this, the
exemption line for Barnegat Inlet will be
relocated slightly east of the current
exemption line to make it consistent
with the 72 COLREGS demarcation line.
NMFS redefines the exemption line
for Delaware Bay as the 72 COLREGS
demarcation line. This is a line drawn
from Cape May Light to Harbor of
Refuge Light; thence to the
northernmost extremity of Cape
Henlopen (Figure 6). Along the
Maryland and Virginia shorelines, two
of the four existing exemption lines
match the 72 COLREGS lines. However,
the exemption line from Chincoteague
to Ship Shoal Inlet crosses the 3nautical mile (5.6-km) state waters line,
which is not consistent with the 72
COLREGS lines. Under this final rule,
NMFS clarifies that the shoreline of
Maryland and Virginia would be
exempted landward of the 72 COLREGS
lines. This includes using the 72
COLREGS line to exempt Chesapeake
Bay. This is a line drawn from Cape
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Charles Light to Cape Henry Light
(Figure 7). In addition, the existing
exemption line for Smith Island Inlet
will be removed from the exempted
waters section of the regulations
because the 72 COLREGS line for
Chesapeake Bay includes the entrance
to this inlet.
The existing exemption lines in the
Southeast (North Carolina to Florida)
will remain unchanged. However,
Captain Sam’s Inlet (South Carolina)
will be added to the exempted waters
section of the regulations because it
does not have a 72 COLREGS line.
NMFS believes that the exemption
lines contained in this final rule are
appropriate in light of the analysis of
the most recent sightings data from
available sources, and will not create a
substantial increase in risk to large
whales from fishing gear. NMFS will
continue to work in collaboration with
state partners to monitor all exemption
areas and should new information
become available regarding the
exemption areas, NMFS will share this
information with the ALWTRT to
determine if changes to the exemption
areas are warranted.
Offshore Exempted Areas
Based on a review of the best
available scientific information, NMFS
has determined that exempting waters at
depths greater than 275 fathoms (1,650
ft or 502.9 m) will not increase the risk
of large whale entanglement in
groundlines, as most large whales are
not known to dive to these depths. To
account for variations in groundline
profiles, NMFS added 5 fathoms (30 ft
or 9.1 m) to achieve an offshore
exemption depth of 280 fathoms (1,680
ft or 512.1 m). Therefore, this final rule
exempts trap/pot and gillnet fishermen
from the requirement to use sinking
and/or neutrally buoyant groundlines in
waters deeper than 280 fathoms (1,680
ft or 512.1 m). Additionally, this final
rule exempts gillnet net panel weak link
and anchoring requirements if the depth
of the float-line is in waters deeper than
280 fathoms (1,680 ft or 512.1 m).
Regulatory Language Changes
Changes listed below are effective on
April 7, 2008 unless otherwise noted.
Weak Links
The ALWTRT recommended that, for
consistency, NMFS should change all
headings for weak links in the ALWTRP
regulations from ‘‘Weak Links on all
Buoy Lines,’’ ‘‘Buoy Weak Links,’’ and
‘‘Buoy Line Weak Links’’ to simply
‘‘Weak Links.’’ Under the ALWTRP final
rule, ‘‘Buoy Line Weak Links,’’ or ‘‘Net
Panel Weak Links’’ will be used for
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clarification. NMFS also clarifies that
weak links must be placed on all
floatation and/or weighted devices, etc.
that are attached to the buoy line, and
not just the main buoy. This final rule
adds to the regulatory text that weak
links must be designed such that the
bitter end (the loose end of the line that
detaches from the weak link) of the line
is clean and free of any knots when the
link breaks, and that splices are not
considered to be knots for the purposes
of this provision. The final rule clarifies
that gillnets, traps/pots, anchors, and
leadline woven into the buoy line are
not considered weighted devices
attached to the buoy line. Therefore,
under this final rule, when referring to
the techniques for meeting the weak
link requirements, the wording will
read, ‘‘All buoys, flotation devices and/
or weights (except traps/pots [or
gillnets], anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc. must be
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
operationally feasible and that meets the
following specifications’’.
In a final rule published on January
10, 2002, the use of line 7⁄16 inch (1.11
cm) in diameter or less for all buoy lines
was removed as an option from the
ALWTRP’s Take Reduction Technology
Lists, as the breaking strength of 7⁄16
inch (1.11 cm) line can vary
dramatically (67 FR 1300, January 10,
2002). Therefore, because the diameter
of line is not appropriate to use for risk
reduction, NMFS will also change the
text that describes the list of approved
weak links. Specifically, the regulatory
text referring to ‘‘rope of appropriate
diameter’’ will be changed to ‘‘rope of
appropriate breaking strength’’.
Where the gear modification
requirements are referred to, this final
rule includes reference to a brochure
that describes techniques for complying
with these requirements and provide
information about how to obtain a copy.
This final rule amends the current
regulatory text describing the placement
of weak links in the floatline of gillnet
net panels. Specifically, the text will be
modified to change the requirements for
the placement of one weak link in
gillnet net panels that are shorter than
50 fathoms (300 ft or 91.4 m). This final
rule modifies the requirements in the
Mid/South Atlantic Gillnet Waters (for
anchored gillnets) and adds
requirements for the Other Southeast
Gillnet Waters as follows: ‘‘Weak links
must be placed in the center of the
floatline of each gillnet net panel up to
and including 50 fathoms (300 ft or 91.4
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m), or at least every 25 fathoms (150 ft
or 45.7 m) along the floatline for longer
panels.’’ This final rule also amends the
requirements for the placement of weak
links in the SAM areas and other
applicable areas where more than one
weak link is required for gillnet net
panels of lengths up to and including 50
fathoms, (300 ft or 91.4 m) as well as
those greater than 50 fathoms (300 ft or
91.4 m). Additionally, this final rule
specifies two configuration options for
gillnet net panel weak links for
anchored gillnet fisheries in the
Northeast (effective April 7, 2008,
including SAM areas April 7, 2008, and
Mid/South Atlantic (that is not returned
to port with the vessel), as well as
gillnet fisheries in the Southeast that are
not returned to port with the vessel
(effective April 7, 2008). See the
requirements for anchored gillnets in
the Other Northeast Gillnet Waters
section of this rule for the specifics on
these configurations for gillnet net panel
weak links. The same configuration
option would be required for all gillnet
net panels in a string.
Groundlines
This final rule clarifies that fishermen
may use sinking and/or neutrally
buoyant line for their groundlines and
buoy lines. Under this final rule, from
January 1 through May 15 fishermen
will be allowed to use sinking and/or
neutrally buoyant groundlines in the
Cape Cod Bay Restricted Area.
Similarly, for the SAM gear
modifications, this final rule will allow
the use of sinking and/or neutrally
buoyant groundlines.
Where sinking and/or neutrally
buoyant line is required for groundlines,
this final rule prohibits the attachment
of flotation devices, such as buoys and
toggles. This clarifies the prohibition on
floating groundlines by expanding the
prohibition to the attachment of any
devices that cause groundlines to float
into the water column, to reduce the
risk of entangling large whales.
Other Regulatory Language Changes
The following changes to the current
ALWTRP regulations are revised to
improve consistency and clarity
(effective April 7, 2008).
Gillnet Take Reduction Technology List
In 2002, NMFS published a final rule
(67 FR 1300, January 10, 2002) that
replaced the Gillnet Take Reduction
Technology List with specific
requirements for gillnet gear in the MidAtlantic; however, the list was
inadvertantly left in the regulations.
This final rule will delete the Gillnet
Take Reduction Technology List.
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Anchoring Clarification
This final rule amends the regulatory
text to clarify how to comply with the
holding power of a 22-lb (10.0-kg)
Danforth-style anchoring requirement
for anchored gillnet fishing gear in the
Northeast, including SAM areas, and
Mid/South Atlantic (that is not returned
to port with the vessel), as well as
gillnet gear in the Southeast that is not
returned to port with the vessel.
SAM Clarification
This final rule clarifies that for gillnet
and trap/pot fisheries, the Stellwagen
Bank/Jeffreys Ledge Restricted Area
overlaps with SAM West boundaries.
Thus, the Stellwagen Bank/Jeffreys
Ledge Restricted Area will be added to
the list of ALWTRP management areas
under the SAM section of the
regulations.
Terminology
For consistency, in the ‘‘Other
Provisions’’ section of the ALWTRP
regulations, this final rule will change
the term ‘‘Cape Cod Bay Critical
Habitat’’ to ‘‘Cape Cod Bay Restricted
Area.’’ In addition, this final rule will
change the name of the ‘‘Southeast U.S.
Restricted Area’’ to ‘‘Southern U.S.
Restricted Area (N and S)’’ (using 29°00′
N. lat. as the dividing line for ‘‘N’’ and
‘‘S’’), and change the name of the
Southeast U.S. Observer Area to the
‘‘Southeast U.S. Monitoring Area.’’
Definitions
The final rule adds definitions to
§ 229.2 for ‘‘bitter end’’ and ‘‘bottom
portion of the line.’’ The ‘‘bottom
portion of the line’’ definition is revised
to clarify the regulatory requirements for
allowing, where applicable, floating line
in a section of the buoy line not to
exceed one-third the overall length of
the buoy line.
The final rule also revises the terms
‘‘Lobster trap’’ and ‘‘Lobster trap trawl’’
to ‘‘Trap/pot’’ and ‘‘Trap/pot trawl’’ to
reflect the broader scope of the
ALWTRP once the new trap/pot
fisheries are included under the
management regime. These definitions
will apply to the trap/pot fisheries that
will be regulated under the ALWTRP.
Prohibitions
The final rule revises the language in
§ 229.3 and § 229.32 regarding the
activities prohibited under the
ALWTRP. Specifically, in paragraphs
(h) through (l) of § 229.3, and where
applicable in § 229.32, NMFS clarifies
that where it is prohibited to fish with
certain gear types, it is also prohibited
to have the gear available for immediate
use. This added language is intended to
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clarify the activities prohibited under
the ALWTRP and improve enforcement.
Also, the phrase ‘‘lobster trap’’ has been
changed to ‘‘trap/pot.’’
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Criteria for Establishing a Density
Standard for Neutrally Buoyant and
Sinking Line and Procedure for
Determining the Specific Gravity of
Line
In response to requests from the
fishing industry and line manufacturers
for a clearer definition of neutrally
buoyant and sinking line, NMFS has
developed criteria for establishing a
density standard for neutrally buoyant
and sinking line and used these criteria
to develop definitions. In addition,
NMFS finalizes a procedure for
assessing the specific gravity of line,
which NMFS will use in the future to
determine whether a manufactured line
meets the accepted density standard.
NMFS’ criteria for establishing the
density standard and procedure to
determine specific gravity of line are
included in the FEIS and available to
the public upon request (see ADDRESSES
for contact information).
This final rule amends the definitions
of ‘‘Neutrally buoyant line’’ and
‘‘Sinking line’’ and clarifies each
definition in relation to groundlines and
buoy lines. Under this final rule,
neutrally buoyant and sinking line will
share the same definition; however, a
distinction will be made to clarify that
sinking and/or neutrally buoyant
groundline could not float in the water
column. Therefore, in this final rule, the
current definition of ‘‘neutrally buoyant
line’’ is amended to mean, ‘‘for both
groundlines and buoy lines, line that
has a specific gravity of 1.030 or greater,
and, for groundlines only, does not float
at any point in the water column (See
also Sinking line).’’ NMFS will keep the
‘‘neutrally buoyant’’ and ‘‘sinking line’’
terms based on industry’s comment that
these are familiar terms that have been
used for a number of years. Accordingly,
the current definition of ‘‘Sinking line’’
is amended to mean, ‘‘for both
groundlines and buoy lines, line that
has a specific gravity of 1.030 or greater,
and, for groundlines only, does not float
at any point in the water column (See
also Neutrally buoyant line).’’
Comments and Responses
NMFS received 81 letters from
commenters on the Draft Environmental
Impact Statement (DEIS) via letter, fax,
or email. Additionally, approximately
25,000 of one type of form letter and 73
of another type of form letter of similar
content were received on the DEIS via
letter and email. NMFS also solicited
comments on the DEIS during 13 public
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hearings held in Virginia, North
Carolina, New Jersey, Maryland,
Florida, Massachusetts, Rhode Island,
and Maine. NMFS received 37 letters
from commenters on the proposed rule
via mail, fax, or email. The comments
are summarized and grouped below by
major subject headings. NMFS response
follows each comment. NMFS received
comments on FEIS technical changes
that were not substantive, and made
changes to the FEIS as appropriate.
These technical comments are not
listed.
General Comments
Comment 1: Some commenters asked
for a more balanced representation of
stakeholders on the ALWTRT.
Specifically, commenters believed that
there should be more seats for
conservationists on the ALWTRT.
Response: The ALWTRT is composed
of Federal agencies, each coastal state
that has fisheries that interact with large
whale species or stocks protected under
the ALWTRP, Regional Fishery
Management Councils, interstate
fisheries commissions, academic and
scientific organizations, environmental
groups, and all commercial fisheries
groups and gear types which
incidentally take large whale species or
stocks. The Marine Mammal Protection
Act (MMPA) states that take reduction
teams shall, to the maximum extent
practicable, consist of an equitable
balance among representatives of
resource user interests and nonuser
interests. The MMPA does not provide
a fixed number or percentage for each
stakeholder group. NMFS believes that
it has an adequate representation of
stakeholders including conservationists.
Comment 2: One commenter
suggested that better results would be
produced by the ALWTRT if issues were
addressed regionally.
Response: At its 2004 meeting, NMFS
provided detailed information on
organizational issues specific to the
ALWTRT. NMFS presented several
options for restructuring the ALWTRT
and the pros and cons of each option.
One option included a regional
component whereby the ALWTRT
would split into two regional teams
(Northeast and Mid/South Atlantic).
However, the ALWTRT did not develop
a consensus recommendation on
formally dividing the ALWTRT into
separate teams by region or other
affiliation. Currently, the ALWTRT is
continuing to meet as a full team, but
NMFS has allocated resources to
conduct small scale regional sub-group
meetings when necessary. In addition,
NMFS has allocated time in its full
ALWTRT meetings for smaller groups
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according to region, gear type, or other
affiliation.
Comment 3: Several comments were
received in support of, as well as in
opposition to, the proposed elimination
of the Lobster Take Reduction
Technology List in Northern Inshore
waters.
Response: As proposed, NMFS has
eliminated the Lobster Take Reduction
Technology List in Northern Inshore
waters and other areas. Eliminating the
Lobster Take Reduction Technology List
in Northern Inshore waters will enable
NMFS to utilize broad-based
management measures in the Inshore
waters. However, NMFS acknowledges
that the elimination of the Technology
List does not preclude NMFS from using
a similar management scheme in the
future if warranted.
Comment 4: Two commenters
requested that all information used in
formulating proposed alternatives and
effectiveness of existing programs be
provided to the public. NMFS should
develop and implement a statistically
reliable methodology for measuring and
reporting serious injury and mortality
rates of all species of marine mammals,
as required by the MMPA.
Response: In support of the proposed
action, NMFS prepared a DEIS. In
accordance with the National
Environmental Policy Act (NEPA), the
DEIS disclosed the purpose and need for
the action; a description of the proposed
alternatives, including a No Action
Alternative; a description of the affected
environment; and a description of the
environmental consequences of each
alternative including any adverse
environmental effects that will be
unavoidable if the proposed action is
implemented. As required by NEPA,
NMFS made all of the information and
analysis contained in the DEIS available
to the public for an 81-day written
comment period and conducted 13
public hearings from Maine to Florida to
receive oral testimony regarding this
action and its supporting information
and analysis. All comments received
during the public comment period and
public hearings were considered in the
FEIS and final rule.
NMFS has developed protocols for
determining large whale serious injuries
and human-caused mortalities. Such
information is contained in mortality
and serious injury determinations
issued by the Northeast Fisheries
Science Center (NEFSC). Human-caused
mortality and serious injury rates
presented in these reports represent the
minimum levels of impact to Atlantic
large whale stocks from 1999–2003
(Waring et al., 2006). Confirmed humancaused mortalities and serious injury
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records from 2000–2004 are also
presented in Cole et al. (2006). Both
reports are available to the public
through the NEFSC publications office
and can also be located online. NMFS
does not attempt to expand data beyond
that which was observed, and at this
time, there is no reliable methodology
that enables NMFS to extrapolate
further from this data.
Comment 5: Two commenters
suggested implementing a ghost gear
removal program.
Response: NMFS does not currently
have the resources to administer and/or
implement such a program. However,
NMFS has supported ghost gear removal
initiatives in the past through its Right
Whale State Cooperative Program,
which is administered through its
partnership with the National Fish and
Wildlife Federation (NFWF), and will
continue to consider future support for
ghost gear removal through this
competitive funding initiative.
Comment 6: Two commenters
suggested that the observer program is
not being used to its fullest potential.
Specifically, one commenter urged
NMFS to prioritize observer coverage for
ALWTRP fisheries. The commenter
believes this would assist in assessing
the effectiveness of gear modifications
and seasonal closures.
Response: Based on the limited
observer resources available and the
competing needs for observer coverage
in many other fisheries, NMFS believes
that the observer program is being used
to the fullest extent practicable given
the resources available and competing
observer needs in other fisheries.
Although NMFS agrees in principle
with the commenter’s suggestion that
increased observer coverage could assist
in assessing the effectiveness of gear
modifications and seasonal closures, the
NMFS observer program is not intended
to be an extension of law enforcement
resources. The National Observer
Program is intended and designed to
collect fisheries dependent physical,
biological, and economic data to assist
NMFS in making management
decisions.
Comment 7: Many commenters
questioned why the Federal
Government is making regulations and
not individual states. Specifically, some
commenters stated that Federal
mandates are not going to work for the
State of Maine while others stated that
there are already state fishery
management plans (FMPs) (e.g., the
State of Florida’s Spanish Mackerel
Plan) that impose rules that are more
protective of whales than the
alternatives proposed by the ALWTRP.
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Response: The MMPA gives NMFS
the authority to administer the
provisions of the MMPA within state
waters. To protect the large whale stocks
included under the ALWTRP from
serious injury or mortality incidental to
commercial fishing interactions, NMFS
convenes the ALWTRT to help develop
appropriate management actions. The
ALWTRT includes each coastal state
that has fisheries that interact with large
whale species or stocks protected under
the ALWTRP. Each state also has
industry representatives who serve on
the ALWTRT. State officials and state
industry representatives have input into
the development of regulations within
state waters. NMFS considered all
comments regarding state fisheries and
areas; this final rule modified certain
provisions within state waters as a
result of these comments.
Comment 8: One commenter stated
concern that more fishermen may fish in
the state exempted areas, which would
create increased gear concentrations in
inshore areas.
Response: In determining the state
exemption lines, NMFS analyzed data
from available sources, including data
that are more current than the data
analyzed for the DEIS. Large whale
sightings distribution data from 1960 to
mid-September 2005 were obtained
from the North Atlantic Right Whale
Consortium (NARWC) Sightings
Database containing dedicated survey
effort and opportunistic sightings data,
which is curated by the University of
Rhode Island (URI), and supplemented
by additional data on humpback and fin
whale sightings. In addition, NMFS
analyzed large whale sightings data
from 2002 through 2006 that were
collected through the NEFSC’s
systematic aerial surveys, as well as
through the Northeast U.S. Right Whale
Sighting Advisory System (SAS). NMFS
also analyzed a right, humpback, and fin
whale sightings database compiled by
the Maine Department of Marine
Resources (Maine DMR), which
includes sightings reported by the
Maine Marine Patrol, whale watch
vessels, etc. Based on this analysis,
NMFS believes that the final exemption
line will provide large whales with an
adequate level of protection. For
example, sightings data along the east
coast indicated that endangered large
whales rarely venture into bays, harbors,
and inlets. Therefore, although gear may
increase in the state exemption areas,
the risk to large whales would be
minimal.
Comment 9: One commenter stated
that NMFS should not regulate Rhode
Island fishermen the same as Cape Cod
Bay fishermen.
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Response: Assuming the commenter
is fishing entirely in Rhode Island
northern inshore waters and comparing
their requirements to fishermen who
fish in Cape Cod Bay during the
restricted period, there are differences
between how Rhode Island and Cape
Cod Bay fishermen are being regulated
under the ALWTRP. Specifically, the
trap/pot gear restrictions and weak link
requirement are different for these areas
and more restrictive in Cape Cod Bay
from January 1–May 15. Also, the
provision to prohibit floating groundline
does not take effect in Rhode Island
until 12 months after publication of the
final rule while the floating groundline
prohibition is already in effect in Cape
Cod Bay for trap/pot fishermen.
Regarding gillnet gear, Cape Cod Bay is
closed to all gillnet gear during the
restricted season while Rhode Island
inshore waters may use gillnets
provided they comply with the
specified gear requirements.
Comment 10: Numerous commenters
believe NMFS should not regulate
fishermen in the Mid-Atlantic/Southeast
the same as those in New England and
believe NMFS should justify new gear
requirements in the Mid-Atlantic and
provide a rationale of why impacts of
new requirements are necessary to
achieve the goals of the ALWTRP. The
commenters believe that regional
management areas should be managed
differently for the following reasons: (1)
Year-round closures are unnecessary in
the Mid-Atlantic area; (2) there are
relatively few right whale sightings; (3)
there is less gear and fewer fishing
vessels; (4) no critical habitat has been
designated in the Mid-Atlantic; and (5)
there are different regional and seasonal
fishing practices in the New England,
Mid-Atlantic, and Southeast fisheries.
Response: The ALWTRP was
developed to reduce the level of serious
injury and mortality of North Atlantic
right, humpback, and fin whales.
Although right whales and humpback
whales are more common in New
England throughout the year, they are
also present in the Mid-Atlantic.
Further, fin whales are common yearround north of Cape Hatteras. Therefore,
NMFS believes all fisheries in these
areas should be subject to similar gear
modification requirements. However,
based on sightings data and comments
received on the proposed rule, NMFS
chose an alternative that allows seasonal
gear restrictions in the Mid-Atlantic as
opposed to year round requirements in
New England. Further, NMFS allowed
small changes to some of these gear
modifications to account for how local
fisheries operate in the Mid-Atlantic
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(see Changes from the Proposed Rule
section of the preamble).
Comment 11: One commenter calls for
a set of regional alternatives rather than
one national alternative for all East
Coast fisheries.
Response: The alternatives examined
in the EIS were the product of extensive
outreach conducted by NMFS. NMFS
reconvened the ALWTRT on April 28–
30, 2003. Proposals from the April 2003
ALWTRT meeting and subsequent
subgroup meetings were used to
develop an issues and options
document, which NMFS made available
to the public during the scoping
process. The scoping document
described the major issues, current
management and legal requirements,
and potential management measures to
address fisheries that may frequently or
occasionally interact with large whales.
During the summer of 2003, NMFS
conducted six public scoping meetings
at locations from Maine to Florida along
the east coast. Based on this outreach
effort NMFS developed a suite of
alternatives that best reflected the
comments from the ALWTRT and
public while at the same time afforded
protection to large whales. The
alternative ultimately selected by NMFS
does include regional measures.
Comment 12: One commenter
believes NMFS needs to look at gear and
effort in different areas. The commenter
believed that regulations are in place
due to problems in Massachusetts, and
if that is where the problem is then that
is where the regulations should be, not
for the entire coast.
Response: Large whale entanglements
are not solely a Massachusetts issue.
Atlantic large whales are at risk of
becoming entangled in fishing gear
because the whales feed, travel, and
breed in many of the same ocean areas
utilized for commercial fishing.
Fishermen typically leave fishing gear,
such as gillnets and traps/pots in the
water for specific periods of time. While
the gear is in the water, whales may
become incidentally entangled in the
lines and nets that comprise trap/pot
and gillnet fishing gear. The number of
entanglements for which gear type can
be identified is too small to detect any
trends in the type of gear involved in
lethal entanglements. However, trap/pot
and gillnet gear are the most common.
NMFS believes that floating groundlines
pose the biggest risk for large whales,
but acknowledges that any type and part
of fixed gear is capable of entangling a
whale throughout its entire range.
NMFS, in consultation with the
ALWTRT, has developed a coast-wide
strategy with regional components to
address entanglements.
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Comment 13: One commenter asked
how many whale entanglements
occurred in traps/pots in 2004.
Response: There were 16 known
entanglements that were first reported
in 2004. However, for most of these, the
actual year of entanglement is not
known. Gear was recovered from seven
of these entanglements. Of the seven
entanglements from which gear was
recovered, five were identified to a
specific gear type. Trap/pot gear
accounted for four entanglements and
gillnet gear accounted for one.
Comment 14: One commenter
believed that it is important that NMFS
listen to the Maine DMR because they
do a good job communicating with
fishermen.
Response: NMFS views all state
representatives serving on the ALWTRT
as valued partners in making sound
management decisions.
Comment 15: Several commenters
believe that fishermen are unlikely to
modify their gear for 9 months, and then
switch to unmodified gear for 3 months.
The commenter believes the economic
burden on the industry would be
relatively the same as year-round
requirements.
Response: Many commenters asked
NMFS to choose seasonal windows
based on large whale distribution. Some
commenters also supported seasonal
requirements due to the occurrence of
seasonal fisheries in some areas.
However, the economic analysis in
Chapter 6 of the EIS assumes that vessel
operators that would be subject to
seasonal ALWTRP requirements would
switch to compliant gear year-round.
Therefore, the implications of seasonal
requirements are accounted for in the
discussion of costs and socioeconomic
impacts. Because the difference in costs
between seasonal and year-round
requirements is low, and the differences
in biological impacts is also low, NMFS
chose seasonal requirements.
Comment 16: One commenter
believes that gillnets should be
prohibited from the Stellwagen Bank
National Marine Sanctuary and the
number of lobster traps and lines should
be limited.
Response: The regulations
implementing the Northeast
Multispecies FMP contain a closure
provision named the Western Gulf of
Maine Closure Area. The closure area
encompasses the vast majority of the
Stellwagen Bank National Marine
Sanctuary. Accordingly, no fishing
vessel or person on a fishing vessel may
enter, fish in, or be in, and no fishing
gear capable of catching NE
multispecies, including gillnet gear,
may be in, or on board a vessel in, the
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Western Gulf of Maine Closure Area.
The Interstate FMP for American
Lobster has also implemented an effort
reduction strategy that limits the
volume of trap/pot gear targeting
lobsters. In addition to the management
efforts in specific FMPs, through this
final action the ALWTRP is
implementing measures that
significantly reduce the risk of an
entanglement and serious injury and
mortality of large whales should an
entanglement occur, such as
implementing a prohibition on floating
groundline for trap/pot and gillnet gear
and an increase in the number of break
away links in the net panels of gillnet
gear. Floating rope between traps/pots,
and the gillnets and anchor systems gear
serves as the greatest risk to large whale
entanglements.
Comment 17: Some commenters
believe that NMFS needs a better
international strategy, otherwise Maine
fishermen are shouldering the burden of
whale conservation. The commenter
believes Maine fishermen take on more
compliance costs than are necessary,
while their counterparts in other
industries and in Canada operate free of
whale take reduction measures.
Response: Since the implementation
of Canada’s Species at Risk Act (SARA),
NMFS has established a strong
relationship with Canada’s Department
of Fisheries and Oceans (DFO) regarding
right whale management. In recent
years, NMFS staff from the Northeast
Regional Office and DFO’s Maritime
Regional Office have met to coordinate
on several critical right whale
management and science issues. Of
particular importance is the
development of a collaborative
approach to managing both gear and
vessel interactions with large whales.
Because of the geographic
concentration of the lobster fishery in
Maine, it is true that Maine vessels bear
a large share of the overall estimated
costs of the ALWTRP modifications.
However, the social impact analysis
suggests that under Alternative 6 Final
(Preferred) only a limited subset of
smaller vessels are likely to experience
costs that represent a large share of
fishing revenues. As reviewed in the
cumulative effects analysis in the FEIS,
fishing gear entanglement and ship
strikes are the two largest contributors
to human-caused whale mortality.
NMFS is currently working on
implementing a ship strike strategy that
will seek to reduce injuries and
mortalities associated with this source.
Chapter 9 of the EIS also reviews a
variety of measures implemented by the
Canadian government. In 2000, DFO, in
cooperation with the World Wildlife
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Fund Canada, developed Canada’s first
Right Whale Recovery Plan and
recovery implementation team. The
recovery plan, which is intended as a
‘‘blueprint’’ for action, includes a
number of recommendations related to
gear entanglement, whale research, and
regulatory and enforcement actions.
Comment 18: One commenter
believes that it is too difficult to
determine what gear modifications will
save right whales. The commenter
believes that there is no one specific
gear modification that we can point to
and say that it is going to save right
whales.
Response: NMFS agrees that currently
there is no one gear modification that
can save right whales. NMFS believes
that the success of the ALWTRP and
right whale conservation depends on a
combination of conservation measures
designed to reduce entanglements and
serious injury and mortality should an
entanglement occur. The ALWTRP
includes a combination of fishing gear
modifications and time/area closures to
reduce whale entanglement in
commercial fishing gear. The nature of
the gear modification requirements
varies by location and time of year,
maximizing reduction in entanglement
risk based on whale distribution and
movement. NMFS complements these
gear modification requirements with
prohibitions on fishing at times and in
places where right whale aggregations
are greatest, and therefore where
entanglement risk may be particularly
high.
Comment 19: One commenter
believed fishermen cannot control ship
strikes or entanglements with fishing
gear that is obviously not from the
Northern Nearshore Lobster Waters
Area. The commenter believes that
Maine fishermen are required to
compromise to fix a problem that they
are not causing.
Response: NMFS is addressing vessel
interactions with large whales through a
separate action (71 FR 36299, June 26,
2006). The number of entanglements for
which gear type can be identified is too
small to detect any trends in the type of
gear involved or the area where the
entanglement occurred. However, trap/
pot and gillnet gear appears to be the
most common gear involved in
entanglements. Based on the limited
information available on entanglements,
NMFS views the entanglement issue as
a coast-wide problem rather than solely
a ‘‘Maine problem’’. Consequently,
NMFS in consultation with the
ALWTRT, has developed a coast-wide
strategy with regional components to
address entanglements.
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Comment 20: One commenter stated
that in Grand Manan Channel, Machias,
Seal Islands, and many areas in Down
East Maine, fishermen cannot operate
under existing requirements (i.e., weak
links cannot hold and fishermen are
constantly replacing poly balls).
Response: In developing the
appropriate breaking strengths for weak
links used by commercial fishermen in
this area, NMFS worked closely with
the ALWTRT, including commercial
fishermen and the state of Maine to
develop what it believes is the
appropriate breaking strength tolerance
for fishermen fishing in this area.
Should new information become
available that may warrant a change to
the weak link tolerances in this area,
NMFS will consult with the ALWTRT
regarding whether to take a subsequent
action.
Comment 21: One commenter
believes that environmentalists are
pushing NMFS to over-regulate and that
fishermen are being put out of business
everyday.
Response: Federal regulations are not
based on pressure from
environmentalists. The purpose of the
revisions to the ALWTRP is to provide
additional conservation and protection
to Atlantic large whales. Such revisions
would fulfill NMFS’ obligations under
the ESA and the MMPA. The need for
the revisions in this final rule is
demonstrated by the continuing risk of
serious injury and mortality of Atlantic
large whales due to entanglement in
commercial fishing gear.
Comment 22: Many commenters
believed that the DEIS is not adequate
for the following reasons: (1) It failed to
follow NEPA requirements; (2) it
disregarded certain comments provided
during the scoping process; and (3) it
lacked an assessment of the biological
benefits to large whales that are likely
to occur as a result of implementing
these modifications to the ALWTRP.
Response: The DEIS complies with all
applicable requirements of NEPA and
contains, among other analyses,
complete assessments of the biological,
social, economic, and cumulative
impacts associated with this action. In
addition, the DEIS summarizes and
integrates the biological, economic and
social impacts analyses allowing for a
broad assessment of the relative merits
of the regulatory alternatives considered
by NMFS. The DEIS also contains a
discussion of the alternatives
considered but rejected by NMFS. The
DEIS summarizes various approaches
and briefly explains why NMFS chose
not to integrate the approach into the
regulatory alternatives under
consideration by NMFS. However,
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based on public comment, some of the
discussions regarding why some of the
approaches were not adopted by NMFS
was expanded upon in the FEIS to better
articulate NMFS’ rationale.
Comment 23: One commenter stated
that the DEIS fails to discuss the ethical
values of whales and the marine
environment, which deserve protection
from human interference and threats.
The commenter believed that DEIS
Chapter 7 in particular discusses social
impact on fishermen’s quality of life,
but shows no contrasting view of
spiritual and intellectual enjoyment of
whales.
Response: Under NEPA, a Federal
agency is not required to consider nonphysical effects such as psychological
effects or moral and ethical values
caused by or in anticipation of a
proposed action. Nonetheless, the
analysis contained in the DEIS does
discuss passive uses as raised by the
commenter. The DEIS discusses passive
use in Chapter 10, the regulatory impact
review section. Chapter 7 of the DEIS
also discusses ‘‘passive uses’’ and
provides a table of passive use studies
related to marine mammals. Language
has been added to the FEIS to clarify
that non-use values such as those
measured in these studies are closely
related to the ‘‘spiritual’’ or ‘‘ethical’’
values emphasized by the commenter.
Comment 24: One commenter
supported continued disentanglement
efforts, such as floating forklifts,
hydraulic slings between two boats, and
an inflatable blanket to keep a subdued
whale afloat.
Response: NMFS appreciates the
support for continued disentanglement
efforts. NMFS recently convened a third
workshop in a series, which included
marine animal experts from numerous
disciplines including, veterinarian
sciences, disentanglement experts,
anesthesiology, marine mammal
behaviorists, etc. to discuss these
suggested approaches as well as many
other options to ascertain which had the
most merit for investigating further
versus which were too cost prohibitive
and logistically impractical. NMFS
reiterates that disentanglement is only a
temporary ‘‘band-aid’’ approach and
that the solution that all involved
parties are striving for is to prevent
entanglement and reduce serious injury
and mortality, if an entanglement
occurs.
Comment 25: Two commenters
believed NMFS did not address minke
whales in the EIS. One commenter said
that the ALWTRP currently does not
consider minke whales, yet the State of
Maine actively trained and equipped
fishermen to disentangle minke whales
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in state waters. The commenter believes
that for the State of Maine to go to such
lengths indicates that these protected
species do become entangled at a
significant rate and that those whales
should be considered under the plan.
Response: The ALWTRP is designed
to protect right whales, humpback
whales, and fin whales. Right,
humpback, and fin whales are strategic
stocks because they are listed as
endangered under the ESA. Therefore,
because these strategic stocks interact
with Category I and II fisheries, under
the MMPA, the ALWTRP was
established to assist in the recovery of
these large whale species. Minke whales
are neither listed as endangered or
threatened under the ESA, nor do they
have high incidental mortalities relative
to population abundance. Therefore,
minke whales are not considered a
strategic stock and are not included
within the ALWTRP. However, the
ALWTRP does provide ancillary
benefits to the minke whale. The minke
disentanglement program is a
component of the Maine’s Large Whale
Conservation Program whereby only a
few commercial fishermen are trained
and authorized to respond to entangled
minke whales. The program was not
developed because of increased takes of
minke whales within state waters.
Comment 26: Several commenters
expressed concern for minke whale
regulations under the ALWTRP. One
commenter believes the potential
biological removal (PBR) for minke
whales may be exceeded based on the
fact that half of the whales stranded
between Maine and Virginia (2002–
2004) showed signs of fishery
interactions. Another commenter
requested that the minke whale stock be
considered ‘‘strategic’’ under the
ALWTRP and for NMFS to continue
current take reduction measures for the
species. The commenter stated that the
status of minke whales in Atlantic
waters is poorly known with more
fishery interactions occurring than that
which is reported. The commenter
states that minke whales are found dead
2 and a half times more than all other
species combined. Another commenter
stated that the Large Whale
Entanglement Report suggests high
entanglement-related mortality. Two
commenters stated that minke whale
carcasses may be less likely to float after
death, thus underestimating serious
injury and mortality.
Response: Stranding data alone do not
provide a reliable base to estimate PBR
and currently, there is no accurate
method to extrapolate further from
stranding data. Minke whales are
neither listed as endangered or
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threatened under the ESA, nor do they
have high incidental mortalities relative
to population abundance. Therefore,
minke whales are not considered
strategic and are not included within
the ALWTRP. However, the species will
still benefit from ALWTRP regulations,
see responses to Comments 4, 25, and
299. It should be noted that minke
whales are the most common species of
baleen whales found in western North
Atlantic waters; estimates suggest that
there may be four times as many minke
whales in these waters as there are
humpback whales. High overall minke
whale abundance may account for the
high incidence of carcass recovery.
Also, there is no current data to either
suggest or support that minke whales
are less likely to float after death when
compared to other large whale species
such as humpback and fin whales.
Comment 27: Numerous commenters
believed there was a lack of discussion
in the EIS regarding how these measures
will be enforced. One commenter
further encouraged NMFS to make
monitoring and enforcement plans a
formal part of a take reduction plan.
Response: At its April 2003 meeting,
the ALWTRT recommended that NMFS
establish a Compliance Committee to
discuss issues such as evaluating,
monitoring, and improving ALWTRP
compliance. The plan development
includes working through the Atlantic
States Marine Fisheries Commission
(ASMFC) and Joint Enforcement
Agreement (JEA) contacts and involves
stakeholder groups on the ALWTRT.
NMFS has made some progress
regarding this issue, particularly with
NMFS and state enforcement offices
through the JEA process. However,
NMFS acknowledges more work is
needed in this area. At its 2004 and
2005 meetings, the ALWTRT also
discussed separating monitoring issues
from the Compliance Committee and
addressing these through a Status
Report Subcommittee. The discussion
focused on the interpretations of the
annual right whale and humpback
whale scarification analysis.
Specifically, the ALWTRT discussed
whether the scarification analysis was
the best method for evaluating the
ALWTRP. NMFS has and intends to
continue these discussions with the
ALWTRT.
Comment 28: One commenter asked
why vertical lines were not addressed in
the DEIS. One commenter believed that
the key elements of a vertical line
strategy could have been articulated in
the DEIS without committing at this
time to specific alternatives.
Response: The proposed changes to
the ALWTRP include some gear
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modifications to vertical line and the
DEIS includes a discussion of vertical
lines. Specifically, the DEIS notes that
further risk reduction to address risk
associated with vertical line will occur
through a future rulemaking action due
to the need for additional information
and discussions to develop
comprehensive and effective
management measures. NMFS and its
partners (e.g., scientific, state, and
industry) are currently researching ways
to reduce risk associated with vertical
line. NMFS and its partners are also
investigating how whales utilize the
water column, including their foraging
ecology and diving behavior, which will
help to determine appropriate
mitigation strategies to reduce
entanglement risk of vertical line. NMFS
has developed a list of potential
management options to reduce risk
associated with vertical line that was
provided to the ALWTRT at its 2005
and 2006 meetings. NMFS discussed
these options with the ALWTRT during
the 2006 meeting and intends to further
discuss these at the next meeting.
Comment 29: One commenter stated
that the agency is balancing the desires
of the industry with the needs of
conservation and the commenter states
this is not appropriate. The commenter
says that the ESA is quite clear that the
needs of the species outweigh economic
impact. The commenter prefers NMFS
to require the institution of the more
risk-averse groundline profile
immediately. It should be coast-wide
and year-round, because whales do
wander.
Response: NMFS believes it is
implementing the appropriate measures
to reduce risk associated with
groundlines, amongst other risk
reduction measures, as quickly as is
feasible and consistent with the
requirements of the ESA. NMFS
believes a phase-in period is warranted
to enable fishermen to rig their gear
with sinking and/or neutrally buoyant
groundline, but believes fishermen will
be continually converting their gear
before the effective date, which will
result in risk-reduction to large whales.
Additionally, NMFS believes that the
coast-wide management approach, with
year-round requirements in the
northeast, and seasonal requirements in
the mid and south Atlantic, is riskaverse. Although whales may be present
outside a seasonal window, the
sightings are rare and the risk of gear to
large whales at these times of the year
is minimal. However, NMFS will
continue to monitor the areas where
seasonal requirements are in effect.
Should new information become
available that indicates that a change in
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seasonal window is warranted, NMFS
will share the information with the
ALWTRT and take appropriate action.
Comment 30: Several commenters
believe NMFS failed to hold hearings in
jurisdictions or locations where groups
other than the industry could be heard.
One commenter requested that the
public comment period on the DEIS be
extended even further, or a
supplemental EIS be issued with
additional hearings held in metropolitan
areas so interested public, advocacy
groups, and the scientific community
can take part.
Response: NEPA provides
opportunities for public involvement at
various stages of the environmental
review process. NMFS held scoping
meetings and public hearings on the
DEIS from Maine to Florida. NMFS
chose areas and locations that were
most affected by the action. NMFS also
solicited public comment through three
open comment periods where comments
could be submitted to NMFS in writing.
NMFS provided an opportunity for the
public to comment during the
publication of its Notice of Intent (NOI)
to prepare a DEIS (68 FR 38676, June 30,
2003), the notice of availability for the
DEIS (70 FR 9306, February 25, 2005),
and the proposed rule (70 FR 35894,
June 21, 2005). The public comment
period of the DEIS was originally 45
days, but was extended to 81 days (70
FR 15315, March 25, 2005) while the
public comment period on the proposed
rule was extended from 31 to 63 days
(70 FR 40301, July 13, 2005). A
summary of all scoping comments and
copies of all written DEIS comments
received by NMFS are found in the
FEIS. NMFS believes that it has selected
appropriate areas for its public hearings
and provided adequate opportunity for
public comment.
Comment 31: One commenter
recommended NMFS prepare a
supplemental DEIS to consider alternate
time/area fishing closures in areas
where right whales and other large
whales congregate, such as critical
habitat. Another commenter
recommended that NMFS develop a
supplemental DEIS to discuss available
information on the frequency of vertical
line entanglements that involved weak
links. The commenter believes that
results of this analysis should be used
to estimate whether, and to what extent,
weak links will reduce the number of
entanglements under each alternative.
Response: NMFS believes that the
DEIS represents a comprehensive suite
of alternatives to amend the ALWTRP as
well as a thorough analysis of the
impacts of the proposed alternatives on
the human environment. NMFS worked
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with the ALWTRT to help evaluate the
ALWTRP and discuss additional
modifications necessary to meet the
goals of the MMPA and ESA. NMFS also
solicited input from the public after
issuing a Notice of Intent to prepare an
EIS. Although there were no consensus
recommendations from the ALWTRT or
consistent proposals from the public,
NMFS believes that it has developed the
best options available for amending the
ALWTRP. NMFS did consider seasonal
closures to prohibit lobster trap/pot and
gillnet fishing in all designated right
whale critical habitats during times
when whales are known to congregate
in those areas. This discussion is
included in the DEIS summary of
written scoping comments received.
This comment is reflected in the section
of the DEIS that lists the alternatives
considered and rationale for rejection,
as well as in the section that describes
the alternatives considered. In the FEIS,
NMFS included additional language to
clarify that this comment was
considered. NMFS has analyzed all
entanglements including those that
involve weak links. Although weak
links are one gear modification that is
included in the current ALWTRP, as
well as a component of the broad-based
gear modifications in the DEIS, NMFS is
not relying solely on this modification.
There is no evidence to suggest that
weak links are ineffective. NMFS
believes weak links, in combination
with other mitigation measures, serve as
a valuable conservation tool.
Comment 32: One commenter stated
that the Southern monkfish area is not
overfished and is not deemed overfished
and this should be fixed in the DEIS.
Response: Monkfish has been
determined by NMFS to not be
overfished in both the northern and
southern areas from 2003 through 2005.
The NEFSC held a monkfish stock
assessment workshop in the fall of 2004
(SAW 40). The data used in the 2004
assessment included NEFSC research
survey data, data from the 2001 and
2004 Cooperative Monkfish Surveys,
commercial fishery data from vessel trip
reports, dealer landings records, and
observer data. The Stock Assessment
Review Committee concluded that the
resource is not overfished in either stock
management area (north or south).
Chapter 4 of the EIS discusses the status
of affected fisheries and does not
indicate that monkfish are overfished.
Therefore, NMFS agrees with the
comment that monkfish is not
overfished in the southern area as of
December 31, 2005. NMFS has changed
the FEIS to reflect this, but has noted
that new information (New England
Fishery Management Council (NEFMC
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and NEFSC 2006 Monkfish Monitoring
Report)) finds that monkfish are now
overfished in both the northern and
southern areas. In the monkfish
Management History section of Chapter
9 of the EIS, the discussion has been
updated to reflect the latest assessment
of the fishery’s status.
Comment 33: One commenter states
ship strike mortalities are not covered in
the DEIS.
Response: Section 118 of the MMPA
requires that take reduction teams
address serious injuries and mortalities
of marine mammals that interact with
commercial fishing operations. The
DEIS is focused on serious injuries and
mortalities of large whales that result
from entanglements in commercial
fishing gear. However, NMFS did
consider ship strike mortality as part of
the cumulative effects analysis in
Chapter 9 of the DEIS.
Comment 34: One commenter wants
NMFS to consider the importance of the
DEIS as NMFS balances the survival of
right whales against development and
commercial interests that can be
modified while still profitable. The
commenter believes that development
and commercial interests can be done in
an environmentally friendly and
commercially viable way. The
commenter also believes that it is the
North Atlantic right whale that may not
survive without NMFS’ strong
protection.
Response: NMFS acknowledges the
commenter and believes that the DEIS
represents a comprehensive suite of
alternatives that has thoroughly
analyzed the impacts of the proposed
alternatives on the human environment
and large whales, including right
whales, as well as other marine mammal
species.
Comment 35: One commenter states
that Exhibit 6–6 identifies potential
sources of increased gear loss, but there
was no specific analysis for gear loss in
rocky/tidal habitats. Further, there is no
analysis for the concept of low profile
groundline in the potential reduction of
gear loss rates. The commenter states
that Exhibit 6–8 states the estimated
change in annual gear loss for Maine
inshore waters in Alternatives 2–4 and
6 will increase by 10-percent; the
commenter states that anecdotal
information says this is a very low
estimation.
Response: As noted in Exhibit 6–6,
the EIS acknowledges that gear loss may
be higher in certain waters such as
rocky bottom areas. Consequently, the
analysis of changes in gear loss rates
separately examines Maine’s inshore
fishery and applies the higher rate of 10
percent. This value represents an
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estimate of the typical change in gear
loss rates for Maine inshore waters;
NMFS acknowledges that some
fishermen will likely experience higher
rates while others will likely experience
lower rates.
NMFS and its partners are actively
researching the use of low profile line
in rocky/tidal habitats to minimize gear
loss; however, additional research is
required before NMFS can determine
whether use of this gear is feasible. See
response to Comment 128.
Comment 36: One commenter
believes that Exhibit 6C–1 does not
seem to account for the useful life of
sinking line in rocky/tidal habitats.
Response: The analysis assumes that
the useful life of sinking and/or
neutrally buoyant line will be lower, on
average, than the useful life of floating
line. This assumption is based in large
part on recognition that the line is more
susceptible to chafing, particularly in
rocky or heavy tide habitats. Adjusting
estimates of the line’s useful life to take
local conditions into account would
introduce a level of detail into the
analysis that is infeasible as it would be
impossible to test in all locations where
groundline could be used.
Comment 37: One commenter
believed that the ESA is relatively blind
to costs of the reasonable and prudent
alternatives of a biological opinion if the
species is in jeopardy.
Response: Regulations implementing
section 7 of the ESA define the criteria
for reasonable and prudent alternatives
(RPA). RPAs must be technologically
and economically feasible. The
ALWTRP is promulgated under the
MMPA. Pursuant to NEPA, NMFS
analyzed the social, biological, and
economic impacts of the various
ALWTRP alternatives on the human
environment.
Comment 38: One commenter
suggested developing a new approach to
eliminate all takes, such as real-time
right whale tracking, improved
reporting of location and amount of gear
in the water, mandatory gear marking,
and effective area closures for trap/pot
and gillnet gear.
Response: The ALWTRT has
discussed many of the commenter’s
concepts in the past. Several of the
commenter’s ideas are currently being
pursued by NMFS and the ALWTRT.
However, a couple of these concepts
need further development. In particular,
real-time right whale tracking has
several limitations both from a technical
and legal standpoint. Monitoring the
location and volume of gear in the water
is also very challenging. Nonetheless,
these ideas have some merit and NMFS
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will continue to discuss these issues
with the ALWTRT.
Comment 39: A few commenters
believed that there are generally no
whales beyond 4–6 miles (7.4–11.1 km)
offshore, so the eastern edge of the
ALWTRP line off of Florida should not
be extended to the Exclusive Economic
Zone (EEZ). Another commenter said
that fisheries in the Southeast occur
greater than 3 nautical miles (5.6 km)
from shore, but most whales are inside
of 3 nautical miles (5.6 km) and in
temperatures greater than 70 °F (21.1 °C)
where most fisheries do not occur.
Response: Habitat models based upon
the aerial survey data collected off the
southeast suggest a strong relationship
between the spatial distribution of
calving right whales, water temperature,
and bathymetry. In particular, calving
right whales were strongly correlated
with water temperatures between 55.4–
59 °F (13–15 °C) and water depths 49.2–
65.6 ft (15–20 m) (Keller et al., 2006;
NMFS unpublished, 2006). However,
southeast spatial distributions and
habitat correlations for non-calving right
whales (e.g., females without calves)
and other large whale species remain
unclear at this time. Sightings data from
the North Atlantic Right Whale
Sightings Database suggest that right
whales, and other large whale species,
do occupy waters greater than 3 nautical
miles (5.6 km) from shore. However,
given the lack of offshore survey effort
in this region, it is possible that there
are more large whales in this area than
reflected in the database. Thus, NMFS
has extended management measures out
to the eastern edge of the EEZ to protect
any large whales in this area, but also
to remain consistent with management
areas extending to the EEZ in MidAtlantic and Northeast waters.
Comment 40: One commenter said
that there is little effort in the shark
gillnet fishery in the Southeast and this
should be acknowledged.
Response: NMFS acknowledges that
gillnetting effort in the Southeast does
not meet or exceed gillnetting levels in
the Mid-Atlantic or Northeast.
Comment 41: NMFS received many
comments supporting year-round, coastwide gear modifications. Comments
supporting this idea included the
following rationale: (1) Right whales
and humpback whales have been seen
as far south as the Carolinas or even
farther south all year long (e.g.,
humpback whales documented feeding
off North Carolina in June 2004); (2) fin
whales have been documented in the
Mid-Atlantic from January through
March; (3) seasonal exemptions seem
linked to survey effort (i.e., there is little
winter/early spring survey effort in
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southern areas); (4) documented
sightings of large endangered whales off
New Jersey (within 20 mile (37.0 km)
radius of Cape May) in summer; (5)
stranding/ship strike data show whales
using waters south of Rhode Island in
summer; (6) Mate data (Mate et al.,
1997) show right whale mother/calf off
New Jersey in August of 1997; (7)
humpback whale strandings in Virginia
and North Carolina have been recorded
in summer; and (8) large whale
movements are unpredictable (e.g.,
Kingfisher went from the southeast to
New England and back again in a few
weeks), therefore, NMFS should
consider updated satellite tracking
information (Baumgartner and Mate,
2005). One commenter questioned the
sighting effort for right and humpback
whales in the Mid-Atlantic during the
late spring/summer and suggested
increased effort in this area; in the
interim, the commenter supported yearround requirements in the Mid-Atlantic.
Response: NMFS has based its
regulations on the best available data
and has considered and incorporated all
sources of available data (e.g., satellite
tracking papers) into this final rule and
the FEIS. NMFS recognizes that animals
occur in Mid-Atlantic waters outside
seasonal management periods, however,
sightings referred to in the above
comments are not typical of the known
ecology of large whales. Expanding
seasonal measures to year-round, coastwide modifications would only offer
minimal risk reduction for large whales
in comparison.
Comment 42: One commenter stated
that whale watch boats operate in the
Mid-Atlantic from April 1 through
November 30. The commenter believes
that if the numbers of whales were
expected to be low from May 31 through
September 1, whale watch boats would
not operate during this time.
Response: Many Mid-Atlantic whale
watching operations conduct tours for
dolphins and other cetacean species.
However, NMFS currently does not
possess data on where such vessels are
traveling or what type of marine
mammals they are observing. Data that
are available to NMFS at this time show
a low sightings record of large whales in
the Mid-Atlantic from June 1 through
August 31. NMFS is not opposed to
receiving new information on large
whales in this area and would welcome
sightings and effort data from MidAtlantic whale watching vessels.
Comment 43: One commenter said
that he takes sea-sampling observers out
everyday and is willing to take someone
with him if it would help determine if
whales are there.
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Response: NMFS appreciates the
support and assistance being offered by
this commenter. Sea-sampling observers
do collect large whale sightings data,
however, this is one of many data
collection responsibilities. If a right
whale is sighted, the sighting is entered
directly into the SAS Right Whale
Reporting System. However, broad-scale
surveys are the best source of
information on the spatial and temporal
distribution of large whales.
Comment 44: One commenter said
that humpback whales can be
consistently found in the Gulf of Maine
during a longer period (April–
December) than indicated in the DEIS.
The commenter also believed that data
presented were obtained by analysis of
a right whale sightings database with
opportunistic data for other large whale
species. The commenter said that
humpback whales have different
ecological characteristics than right
whales and do not use the same feeding
habitats concurrently. The commenter
believed that opportunistic sightings
data may not paint a representative
picture of the spatial and temporal
distribution of humpback whales.
Response: NMFS has modified the
FEIS to reflect this comment. However,
NMFS did not analyze only
opportunistic sightings data when
analyzing the distribution of other large
whale species. Systemic sightings data
(e.g., NMFS survey data), are
incorporated into the NARWC Database
(curated by URI). These aerial and
vessel surveys are conducted
throughout the Atlantic coast, and
although many surveys are focused on
right whale documentation, many other
surveys are conducted to sight and
record the location of other large whale
species or marine mammals.
Comment 45: One commenter
believes whales that get entangled are
sick, which inhibits their ability to
navigate around gear. The commenter
further believes whales get entangled in
ghost gear (e.g., trailing lines and
refuse).
Response: Currently there is no data
to support this hypothesis. Scarification
analyses indicate a large percentage of
whales interact with fishing gear, with
most surviving these encounters. Also,
at this time, NMFS cannot state
conclusively that whales are becoming
entangled in ghost gear.
Comment 46: One commenter wanted
to know if the economics and
technological feasibility of
implementation had been considered.
Response: The specific meaning of the
‘‘economics and technological
feasibility of implementation’’ is
unclear. The commenter may refer to
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the public sector cost of administering
and enforcing the proposed rules; such
an analysis is not required in an EIS.
Alternatively, the commenter may be
referring to the economic impact of the
proposed alternatives on the fishing
industry, a subject addressed
extensively in the EIS. Chapter 6
estimates per-vessel and industry-wide
incremental costs for affected fisheries.
Chapter 7 considers the socioeconomic
impact of the alternatives, i.e., what
geographic areas are most affected and
will the regulations affect the economic
viability of fishing operations.
Furthermore, the regulatory flexibility
analysis (Chapter 11) focuses on the
implications of the rules for small
business.
General Comments on Proposed
Alternatives
Comment 47: NMFS received many
comments stating that none of the
proposed alternatives would sufficiently
protect large whales for several reasons
that include: (1) The proposed
regulations will not achieve PBR; (2) the
proposed actions may not achieve the
goals of the MMPA; and (3) proposed
regulations need to be strengthened, as
it is NMFS’ mandate under the ESA.
Response: NMFS disagrees with the
commenters’ assessment that none of
the proposed alternatives would
sufficiently protect large whales. NMFS
believes that the EIS represents a
comprehensive suite of alternatives to
amend the ALWTRP as well as a
thorough analysis of the impacts of the
proposed alternatives on the human
environment. NMFS worked with the
ALWTRT to help evaluate the ALWTRP
and discuss additional modifications
necessary to meet the goals of the
MMPA and ESA.
Comment 48: Numerous commenters
stated that more time is needed to
evaluate whether the current plan is
working. Many believed that other
ALWTRP measures (i.e., weak links,
critical habitat closures, buoy
modifications, and limited time-area
closures) should be properly evaluated
to determine their effectiveness before
implementing a prohibition on floating
groundlines.
Response: Since right, humpback, and
fin whales are listed as endangered
species under the ESA, they are
considered strategic stocks under the
MMPA. In response to its obligations
under the MMPA, NMFS established the
ALWTRT to develop a plan for reducing
the incidental take of large whales in
commercial fisheries to below the PBR.
PBR for right whales is set at zero.
Consequently, if any right whale is
entangled in commercial fishing gear
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that has been determined to be from the
sink gillnet or pot/trap gear, NMFS must
take additional action to protect right
whales. Evaluation of implementation
and effectiveness of existing measures is
ongoing; however, since serious injury
and mortality of large whales in
commercial fisheries exceeds PBR,
NMFS needs to take additional action in
response to its requirements under the
MMPA.
Comment 49: Some commenters
stated that until research shows how,
when, and where whales become
entangled in fishing gear, none of the
alternatives should be implemented.
One commenter believes research is
needed regarding where and when
whales are most at risk. Otherwise, the
commenter believes a new management
plan may be ineffective to protect
whales, while also causing economic
hardship to fishermen. The commenter
believes new rules must be based on the
most recent data and build in flexibility
to generate new data for consideration.
Response: The FEIS notes that
entanglements of large whales are still
occurring in sink gillnet and trap/pot
gear and highlights the legal mandates
of the MMPA and ESA that NMFS is
required to follow. Based on the
continued serious injury and mortality
of large whales due to entanglement in
these gear types, NMFS must take action
to provide more protection to large
whales. Although NMFS acknowledges
a need for more scientific information,
NMFS is required to take action based
on the best information that is available
when developing the EIS. As new
information becomes available regarding
large whales, entanglements, or
commercial fishing gear modifications,
NMFS will share this information with
the ALWTRT to determine if additional
changes to the ALWTRP are warranted.
Comment 50: Several commenters
urged NMFS to develop whale rules
with as much flexibility as possible,
allowing for innovations to be
implemented as they are developed.
One commenter believes that as NMFS
constructs the final rule for this Plan,
the agency should adopt a flexible and
adaptive approach, and continue
refining the regulations on a region-byregion basis. The commenter also
believes that, considering our limited
understanding of large whale ecology
across diverse habitats, as well as the
variability among the dozens of different
fixed gear fisheries along the Atlantic
seaboard, the Plan must be flexible and
responsive to changing ecological and
economic conditions over time.
Response: NMFS acknowledges this
very important comment and will
continue to work with the ALWTRT and
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with its legal mandates and
requirements to help facilitate better
flexibility within the ALWTRP
regulations. NMFS has developed and
implemented flexible regulations in the
past, but learned that the mandates and
requirements that NMFS must follow
limited NMFS’ flexibility and ability to
react quickly. In addition, in many
instances, NMFS is also limited by the
lack of information available to
implement flexible regulations. NMFS
will continue to explore the concept of
flexible rulemaking with the ALWTRT.
Comment 51: One commenter stated
that the 2001 biological opinions on the
American Lobster, Multispecies, Spiny
Dogfish, and Monkfish FMPs make clear
that unless the agency identifies an
alternative that would eliminate
entanglement and ship strikes, the
alternative is unlawful.
Response: The 2001 Biological
Opinion included an RPA composed of
several measures that were subsequently
incorporated into the ALWTRP. The
Biological Opinion also included
criteria to monitor the RPA’s
effectiveness. The RPA and monitoring
criteria are based solely on right whale
entanglements with commercial fishing
gear, not ship strikes. Ship strikes are
evaluated through a separate action in
support of the implementation of the
national right whale ship strike strategy.
At that time, the 2001 Biological
Opinion concluded that the RPA was
sufficient to allow the commercial
lobster trap/pot fishery to continue.
However, since that time NMFS has
reinitiated consultation on the
continued implementation of the
American lobster fishery in federal
waters based on new information on the
effects of the fishery on right whales.
This consultation is ongoing. NMFS will
consider changes to the ALWTRP
during consultation on the American
lobster fishery.
Comment 52: One commenter asked
how many lethal takes are expected to
occur under the status quo and how
many lethal takes are expected to occur
under each alternative.
Response: NMFS cannot predict how
many lethal takes are expected to occur
under each alternative. The evaluation
of the impact of regulatory changes on
whale entanglement risks is largely
qualitative. This approach is necessary
because models that would enable
NMFS to conduct a rigorous
quantitative assessment of such risks do
not exist. The known threat that
commercial fishing poses to large
whales is the risk of incidental
entanglement in commercial fishing
gear. The regulatory changes under
consideration are designed to reduce
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harm to large whales by reducing the
likelihood of entanglement and/or
reducing the severity of an
entanglement should one occur. NMFS
seeks to achieve these objectives
through a combination of two general
measures: (1) Gear modification
requirements; and (2) restrictions on
fishing activity at specified locations
and times. Chapter 5 of the EIS
examines the impact of these measures
on whale entanglement risks.
Comment 53: Several commenters
disagreed with NMFS’ conclusion that
gear modifications were necessary for
tended and/or actively fished net
fisheries.
Response: NMFS specifically
requested public comment on whether
gear modifications were warranted for
gear that is tended and/or actively
fished. NMFS is not implementing the
proposed weak link requirement for
tended driftnet gear at this time due to
potential safety issues that were raised.
Thus, NMFS believes further research
on this fishery, and specifically testing
weak links in drift gillnet gear, is
needed before weak links should be
required.
Comment 54: One commenter
suggested the alternatives should be
harmonized with other federal mammal
protection plans (e.g., the bottlenose
dolphin protection plan) to prevent the
possibility of creating several plans each
with their own unique requirements.
Response: Chapter 9 of the EIS
includes a cumulative effects analysis
that examined the impacts of this action
in conjunction with other factors that
affect the physical, biological, and
socioeconomic resource components of
the affected environment. The purpose
of the cumulative effects analysis is to
ensure that Federal decisions consider
the full range of an action’s
consequences, incorporating this
information into the planning process.
The cumulative effects analysis studies
the impacts of the regulatory
alternatives to other federal marine
mammal take reduction plans and
fisheries management plans within the
context of other past, present, and
reasonably foreseeable future actions.
Comment 55: Several commenters
believed that the proposed rule should
not apply to Florida gillnet fisheries for
several reasons: (1) Some non-shark
fisheries currently use rope that has a
breaking point of 800 lb (362.9 kg), well
below the 1,100-lb (499.0-g) weak link
breaking point indicated in the take
reduction plan; (2) night fishing is
allowed only if strike nets are deployed
(strike nets are set in a circle and sink
two to five feet (0.6 to 1.5 m) below
water; the net is then retrieved); (3)
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anchored gillnets are not used by
Florida fisheries; (4) sinking or neutrally
buoyant line is already used on buoys;
and (5) gillnets are always tended (i.e.,
within eyesight of fishermen).
Response: NMFS acknowledges that
some gillnet fisheries conducted off the
coast of Florida may already use gear
that is more restrictive than that gear
proposed in the EIS. However, NMFS
believes that there are several new and
emerging fisheries that do not prescribe
to the gear requirements noted by the
commenter. This final rule will regulate
several new fisheries under the
ALWTRP through the Category I and II
annual list of fisheries process
implemented under the MMPA. The
final rule provides protection to large
whales from these new and emerging
fisheries and, at the same time, ensures
that the current fisheries have an
established baseline for large whale
protection.
Comment 56: One commenter
supports the implementation of a pre1997 status quo.
Response: A pre-1997 status quo
option was not analyzed in the DEIS.
Section 118 of the MMPA requires that
NMFS reduce bycatch of strategic
marine mammal stocks incidentally
taken during commercial fishing
operations. The level of documented
serious injury and mortality of right,
humpback, and fin whales due to
entanglement in fishing gear required
NMFS to convene a take reduction team
and develop a take reduction plan to
protect these whales. This final rule
implements modifications to the
ALWTRP, which are necessary because
NMFS has evidence that serious injury
and mortality in commercial fishing
gear is still occurring at unsustainable
levels.
Comments Specific to Each Alternative
Comment 57: NMFS received
numerous comments in support of
Alternative 1. Commenters believed
NMFS has not provided data to show
there is a problem that warrants
amending the current ALWTRP. Other
commenters thought existing
regulations have not been given enough
time to work. One commenter also said
that economically, in today’s dollars, it
would probably cost $8,000 to replace
groundline as proposed in the other
alternatives, and the way that the
material is increasing in price, costs
could be greater than $10,000 by 2008.
Response: NEPA requires NMFS to
analyze a no action alternative
(Alternative 1). NMFS did not choose to
finalize this alternative because it does
not adequately protect large whales, and
therefore, does not satisfy the
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requirements of the MMPA or ESA. Due
to the endangered status of the North
Atlantic right whale population, and the
insufficiency of existing measures in
addressing right whale mortality, there
is a need to further reduce serious injury
and mortality. NMFS has determined
that the additional regulatory measures
included in this action are necessary to
meet the objectives of the ESA and the
MMPA. The ESA requires that NMFS
ensure that activities it authorizes,
including commercial fishing, do not
jeopardize the continued existence of
endangered and threatened species. The
MMPA provides that the immediate goal
of a take reduction plan is to reduce
incidental mortality and serious injury
of marine mammals taken in the course
of commercial fishing to levels less than
the PBR level and the long-term goal is
to reduce such incidental mortality and
serious injury to insignificant levels
approaching a zero rate. These
regulatory changes are necessary to
attain these goals.
The costs associated with converting
to sinking and/or neutrally buoyant
groundline will vary by vessel,
depending on the quantity of gear
fished. The $8,000 to $10,000 range
specified by the commenter may be
valid for certain vessels. In the FEIS,
gear replacement costs have been
revised to incorporate up-to-date data
on key inputs such as groundline.
Chapter 7 of the EIS identifies vessel
segments that may be heavily impacted
by comparing average vessel revenues
with compliance costs. The analysis
suggests that under Alternative 6 Final
(Preferred), a limited number of small
vessels are most at risk. Although costs
are high for some vessels, NMFS made
modifications to the final rule, based on
public comment, to decrease costs
where possible while still meeting its
goals under the MMPA and ESA (see
Changes from the Proposed Rule section
of the preamble). While these vessels
may still realize high costs relative to
revenues, fishermen have some options
to try to mitigate the costs. For example,
the impacts of converting to sinking
and/or neutrally buoyant groundline
may be defrayed, in part, by current and
future groundline buyback programs
operated by NMFS and other partners.
In addition, although the requirements
under Alternative 6 Final (Preferred)
may impose significant costs within the
first year after publication of the final
rule (to convert all groundline to sinking
and/or neutrally buoyant groundline),
fishermen may be able to distribute the
cost of the new gear over its useful life
by seeking a loan. After the first year,
ongoing costs would be significantly
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lower as fishermen would only need to
replace worn-out and lost gear.
Comment 58: NMFS received a
comment opposing Alternative 1.
Response: NMFS agrees with the
commenter (see response to Comment
57).
Comment 59: One commenter
supports Alternative 1 until the
shipping industry and Navy have been
regulated so their take is considerably
less than it is now.
Response: NMFS recognizes that other
marine resource users such as the
shipping industry and the U.S. military
are impacting large whale species, and
NMFS is simultaneously pursuing
various regulatory and non-regulatory
means of addressing the ship strike
issue (see response to Comment 279).
However, serious injury and mortality to
large whales due to entanglement
continues to occur under the current
regulations, and as such, NMFS must
continue to address the impact by
modifying the ALWTRP as appropriate.
Comment 60: Numerous commenters
expressed support for Alternative 2
stating that it is the only option that
truly affords large whales protection
from the risk of entanglement.
Response: Alternative 2 is the most
conservative, risk-averse approach to
the protection of endangered whales
because it would require year-round use
of low-risk gear along the entire Atlantic
coast. However, based on the available
sighting information the potential for
entanglement of whales in the MidAtlantic or South Atlantic waters during
summer months is minor. Therefore, the
year-round requirements provided in
Alternative 2 would likely offer a
minimal risk reduction benefit relative
to NMFS’ preferred alternative,
Alternative 6 Final, which incorporates
seasonal requirements based on
sightings data documenting the
movements of large whales.
Comment 61: NMFS received several
comments objecting to Alternative 2. In
addition, one commenter proposed
specific changes to Alternative 2
regarding the number of traps per trawl
in specified areas.
Response: NMFS agrees with the
commenters (see response to Comment
60). NMFS has reverted back to the
status quo for the number of traps per
trawl in specified areas.
Comment 62: Several commenters
expressed support for Alternative 3. One
commenter supported the alternative
because it incorporates seasonal
components. Another commenter would
only support Alternative 3 if the MidAtlantic northern boundary was moved
to the southern border of Delaware, in
order to better protect whale habitat.
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Conversely, NMFS received many
comments objecting to Alternative 3.
One commenter believed its
requirements may cause effort to shift
into exempted areas. The commenter
believes the line drawn from Watch Hill
Point, RI (41°18.2′ N. lat. and 71°51.5′
W) south to 40°00′ N. is arbitrary and
not sufficiently protective of right
whales, which have sometimes been
seen west of 72°00′ W. The commenter
states that NMFS used sightings data to
determine this line, but those data are
not included in the DEIS. Further, the
commenter believes a more regional
management approach is prudent and
suggested that NMFS analyze
incorporating the ‘‘Middle Zone’’
boundary.
Response: The DEIS identified
Alternative 3 as one of its preferred
alternatives because of the risk
reduction benefit of implementing
broad-based gear modifications on a
seasonal basis. NMFS did consider
implementing Alternative 3 along with
the commenters proposed change to the
northern boundary of the Mid-Atlantic
area. However, the available sighting
information did not support the
proposed change to the Mid-Atlantic
boundary. At this time, NMFS considers
waters south of Watch Hill Point, RI
(41°18.2′ N. lat. and 71°51.5′ W) to have
a seasonality for Atlantic large whales
(e.g., migratory corridor). Although
animals may be present in Mid-Atlantic
waters outside the seasonal period
defined in this final rule, recorded large
whale sightings are rare at that time for
waters south of Long Island Sound.
Thus, moving the northern boundary of
the Mid-Atlantic management area to
the southern border of Delaware would
not offer substantial risk reduction for
large whales. However, NMFS will
reconsider such measures if it receives
additional data for such areas and
seasons. In addition, NMFS believed
that Alternative 6 also offered more
immediate protection to right whales
and identified this as the other preferred
alternative in the DEIS.
NMFS recognizes that there have been
sightings of right whales west of 72°00′
W.; however, such events are
uncommon. The seasonal variation in
gear modification requirements is based
on whale distribution data in NMFS’
analysis of the NARW Sightings
Database through early 2003,
supplemented by additional data on
humpback and fin whale sightings.
Comment 63: NMFS received several
comments in support of and in
opposition to Alternative 4.
Response: Alternative 4 is one of the
more risk-averse approaches to the
protection of endangered whales
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because it would require year-round use
of low-risk gear from the coast of Maine
through the South Carolina/Georgia
border and seasonal restrictions off the
coast of Georgia and Florida. However,
based on sighting information, the
potential for entanglement of whales in
the Mid-Atlantic waters during summer
months is low. Therefore, the yearround requirements provided in
Alternative 4 for the waters off the MidAtlantic coast would likely offer a
minimal risk reduction benefit relative
to NMFS’ preferred alternative,
Alternative 6 Final, which incorporates
seasonal requirements based on
sightings data documenting the
movements of large whales.
Comment 64: NMFS received many
comments in support of Alternative 5.
Most comments in support of
Alternative 5 were from the commercial
fishing industry from Maine. Many of
these commenters supported Alternative
5 only if the status quo alternative
(Alternative 1) could not be maintained.
Others believed Alternative 5 best
suited fishermen in Maine because
Maine fishermen would only have to
shoulder a small fraction of the
compliance costs under this alternative
as compared to the other alternatives.
One commenter believed that
Alternative 5 has the least impact on
Maine fishermen while still meeting
baseline whale protection goals of the
ALWTRP. Two state representatives and
several other commenters supported
Alternative 5 as it did not prohibit the
use of floating rope. Similar comments
were also received from fishermen from
the Mid-Atlantic and Southeast.
Response: As noted in the response to
Comment 57, the status quo Alternative
1 does not adequately protect large
whales resulting in NMFS
determination that regulatory changes
are necessary to attain the goals of the
ESA and MMPA. Of the remaining
alternatives considered, NMFS believed
that Alternative 5 was the least
conservative, risk-averse approach to
the protection of endangered whales.
Although the SAM area was proposed to
be expanded beyond what is currently
required, the use of low-risk gear (e.g.,
prohibition on floating groundline) was
only required in a relatively small area
along the entire Atlantic coast. Thus,
NMFS believed Alternative 5 offered
less protection to large whales
compared to the final preferred
alternative because the risk of serious
injury and mortality is greater under
Alternative 5 and less likely to obtain
the goals under the ESA and MMPA.
Most fishermen seemed to prefer
Alternative 5 based primarily on
economic impacts. By adopting
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Alternative 5, the cost of compliance
would be shifted to fishermen who fish
within the smaller SAM area. However,
based on the available sighting
information, NMFS believes the
potential for entanglement of whales
can occur outside of SAM areas.
Although Alternative 5 produces the
lowest economic effect to industry, it
provides a lower risk reduction benefit
compared to both the seasonal and area
requirements provided under NMFS’
preferred alternative, Alternative 6
Final, which is based on the movements
and sightings of large whales.
Comment 65: The States of
Connecticut and New York concurred
with NMFS’ determination that the
proposed measures are consistent with
the state’s Coastal Zone Management
(CZMA) Program, provided that NMFS
exempt Lobster Management Area 6
(LMA 6) from the requirements of the
ALWTRP. They noted that the available
sightings information indicates that
large whales do not frequent this area
and there is a significant increase in the
risk of gear loss. They further identified
Alternative 5 as its first preference, but
noted that should NMFS not select
Alternative 5, that they would favor
Alternative 6.
Response: NMFS reviewed the
available sightings information within
LMA 6 and determined that the
potential for entanglement of whales is
low in this area while the potential for
gear loss is high. Therefore, NMFS has
expanded the exemption line in Rhode
Island sound to extend from Watch Hill,
Rhode Island, to Montauk Point, New
York. As noted in the response to
Comment 64, NMFS believes
Alternative 5 provides a lower risk
reduction benefit compared to both the
seasonal and area requirements
provided under NMFS’ final approved
Alternative 6, which is based on the
movements and sightings of large
whales.
Comment 66: Several commenters
objected to Alternative 5 stating that it
is the least protective alternative to
protect large whales.
Response: Not including the status
quo Alternative 1, NMFS agrees that
Alternative 5 was the least conservative,
risk-averse approach to the protection of
endangered large whales and did not
select this alternative in the final rule.
Comment 67: One commenter stated
that Alternative 5 does not include a
phase-in of gear modification
requirements (i.e., there are no broadbased gear modifications outside of
expanded SAM). The commenter
believes that NMFS should justify this
by showing the level of risk reduction
for Alternative 5 with respect to other
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alternatives, or how risk reduction
deficiencies would be compensated
elsewhere.
Response: Chapter 5 of the EIS
provides a detailed discussion of the
risk reduction associated with
Alternative 5 relative to the other
alternatives. Consistent with the
comment, Chapter 5 concludes that the
absence of broad-based gear
modification requirements in
Alternative 5 would result in lower risk
reduction benefits for large whales.
Comment 68: One commenter
believes that if NMFS were to
implement Alternative 5, SAM areas
may be further expanded even more in
the future.
Response: The SAM area developed
in Alternative 5 was based on the best
sightings information available.
However, had NMFS selected
Alternative 5, NMFS could have
modified the SAM area through a
separate rule if an expansion of the
SAM area was warranted.
Comment 69: A commenter
recommended that if Alternative 5 is
selected it should be effective
September 1–March 31 in the MidAtlantic. The commenter pointed out
that year-round closures are
unnecessary in the Mid-Atlantic area
(especially around New Jersey) since
sightings of large whale tend to occur
between January and March.
Response: Seasonal gear
modifications for the Mid-Atlantic will
be required from September 1–May 31,
as defined in this final rule. At this time
of year, large whales primarily occur
and are still migrating from southern
waters to northern feeding grounds
(through April and May). NMFS
believes that implementing regulations
through March 31 would not offer
adequate protection.
Comment 70: Several commenters
believed that Alternative 5 was
impracticable because it required 600lb. (272.2-kg) weak links for vertical
lines, which would snap in heavy tides
and lead to more ghost gear (i.e., gear
lost at sea).
Response: There is no 600-lb. (272.2kg) weak link requirement for vertical
lines. The 600-lb. (272.2-kg) weak link
requirement is for flotation and/or
weighted devices added to the vertical
line. Due to results from load-testing
analyses, NMFS believes these breaking
strengths are appropriate.
Comment 71: NMFS received a few
objections to Alternative 6; one
commenter opposed Alternative 6
because of the seasonal component of
the broad-based gear modifications.
However, numerous other commenters
expressed support for Alternative 6. One
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commenter asked that NMFS only apply
Alternative 6 where whales have been
sighted.
Response: NMFS believes that
Alternative 6 (Final) offers the best risk
reduction benefit to protect endangered
whales because it requires the use of
low-risk gear in areas and times shown
to have a high abundance of large
whales. Because of their migratory
patterns, large whales are primarily
present in Mid- and South Atlantic
waters during particular months while
they appear to be in New England
waters on more of a year round basis.
Alternative 6 (Final) requires low-risk
gear on a seasonal basis for fisheries in
the Mid- and South Atlantic while
requiring low risk gear on a year round
basis in the New England area.
Comments on Exemption Lines/Areas
Comment 72: One commenter
believed exemption lines should be
proposed by state governments.
Response: As part of the scoping
process provided under NEPA, NMFS
conducted several scoping meetings
throughout the Atlantic coast. At each
meeting, NMFS made available a
scoping document that contained issues
and options for modifications to the
ALWTRP. The document contained a
section concerning exemption areas and
requested input from the general public,
including state representatives on the
ALWTRT, to identify exemption areas.
The proposed exemption areas have
been developed in response to requests
from state fishery management agencies,
as well as others, and are designed to
ensure that the ALWTRP does not
unnecessarily extend commercial
fishing regulations to waters in which
endangered or protected whales have
been rarely, if ever, observed. However,
partially based on the comments
submitted by interested states, NMFS
modified the proposed exemption areas.
The Changes from the Proposed Rule
section of the preamble discusses these
exemption line changes. NMFS will
continue to monitor all exempted areas,
and encourage states to develop
contingency plans in the event a large
whale is sighted in such areas.
Comment 73: Many commenters
supported using the International
Regulations for Preventing Collisions at
Sea (COLREGS) to base exemption lines.
However, one commenter did not
support using the COLREGS in
Buzzards Bay and Long Island Sound
and requested NMFS to review large
whale sightings and reconsider these
exemptions. Another commenter stated
there is little evidence to support
exempting Buzzards Bay and Cape Cod
Canal from gear modification
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requirements because sightings data
corroborate that whales do occur in both
areas.
Response: NMFS reviewed the large
whale sightings for Long Island Sound
and has amended the proposed
exemption line. The new exemption
line runs from Watch Hill, RI, to
Montauk Point, NY. Based on
comments, NMFS will revert to the
status quo exemption lines for
Massachusetts, which includes
Buzzards Bay. Thus Buzzards Bay will
not have an exemption at this time. See
response to Comment 77 for more
specific information about
Massachusetts.
Comment 74: Many commenters
believe that there need to be exemptions
within 3 nautical miles (5.6 km). One
commenter stated that the considered
regulations seem unfair and unsafe for
those fishing near the shore, where they
said whales are not seen. Several other
commenters believed that SAM areas
should not exist inshore of 3 nautical
miles (5.6 km) due to the fact that no
whales have been seen within 3 nautical
miles (5.6 km) of shore.
Response: NMFS has received many
reports throughout New England and
the Mid-Atlantic detailing numerous
sightings of large whales within 3
nautical miles (5.6 km) of shore.
Therefore, NMFS does not believe
exemptions within the 3 nautical mile
(5.6 km) line along the coast would
provide adequate protection for large
whales and is not appropriate at this
time.
Comment 75: One commenter stated
that NMFS has no means to require
modifications if whale habitat use
changes (e.g., if fisheries expanded to
> 280 fathoms (512.1 m or 1,680 ft) or
if right whale habitat use changes due
to potential climatic shifts. Such
changes could result in whales using
proposed exempted areas, such as
Delaware and Chesapeake Bays.
Response: Should new information
become available that indicates that a
change in the inshore or deep water
exemption areas is warranted, NMFS
will share the information with the
ALWTRT and will take appropriate
action.
Comment 76: One commenter
believes the 280 fathom (512.1 m or
1,680 ft) groundline exemption should
be flexible and revisited when the
agency has more research information
and sightings data.
Response: Currently available dive
data suggest that large whales do not
dive deeper than 280 fathoms (512.1 m
or 1,680 ft). Data come from world-wide
observations and are not limited to the
Gulf of Maine. As with all exempted
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areas, if NMFS is presented with new
information on the diving behavior of
large whales along the east coast that
calls the 280 fathom (1,680 ft or 512.1
m) depth level into question, then it will
revisit regulations in waters greater than
280 fathoms (512.1 m or 1,680 ft) if
necessary. See Comment 75.
Comment 77: Several commenters
oppose the proposed exemption line for
Massachusetts for the following reasons:
(1) It would cause a safety issue as there
are 8,000 recreational lobstermen in the
state and enforcing ALWTRP
requirements so close to shore could be
dangerous; (2) the proposed area is too
small to benefit fishermen; and (3)
nearly all trap/pot fishermen who fish
in the exempted area have received a
75-percent subsidy to convert to sinking
groundline, therefore, exempting these
areas would be difficult to explain and
enforce.
Response: NMFS agrees with the
concerns raised by the commenters and
therefore did not adopt the proposed
expansion of the exemption line within
Massachusetts state waters. Should new
information become available to
alleviate these concerns, NMFS in
consultation with the ALWTRT, may
take future action to modify the
exemption line.
Comment 78: Numerous commenters
expressed concern for exemptions in the
area known as ‘‘the Race’’ in
Connecticut and New York. The
commenters suggested that waters west
of a straight line drawn from Montauk
Point, Long Island, to Watch Hill, Rhode
Island (current Lobster Management
Area 6 line), should be excluded from
the proposed amended ALWTRP.
Response: Discussed in response to
Comment 65, NMFS reviewed the
available sightings information within
LMA 6 and determined that the
potential for entanglement of whales is
low in this area while the potential for
gear loss is high. The data revealed that
large whales are rarely sighted near the
mouth of Long Island Sound and there
are no documented interactions between
whales and fishing gear in this area.
Upon further inspection NMFS found
that this area falls on either side of the
current exemption line and has
exceptionally strong currents with
varying depths and very rocky
topography. This area also has high
vessel traffic where gear loss is already
common. NMFS believes that the use of
sinking groundline and 600-lb (272.2kg) weak links in this area coupled with
the issues noted above would increase
this gear loss and create a safety risk to
fishermen. Consequently, NMFS has
modified the exemption line in Long
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Island Sound to run from Watch Hill,
RI, to Montauk Point, NY.
Comment 79: One commenter
recommended that NMFS check the
accuracy of Exhibit 6H–1. The
commenter stated that Connecticut
fishermen operate in waters other than
Connecticut waters; they report
commercial fishing activities outside of
Connecticut waters to the CTDEP and
they fish in the ‘‘Race’’ under New York
non-resident commercial lobster
licenses. The commenter believes the
assumption in Exhibit 6H–1, that vessel
activity for state-permitted vessels is
equally distributed only within state
waters, is not accurate. Also, the
commenter believes Exhibit 6G–2 is not
accurate because, although there are
fishermen who operate in Connecticut
waters inside Long Island Sound, which
is exempted, there are also vessels that
fish in the ‘‘Race’’ and are affected by
ALWTRP requirements.
Response: NMFS recognizes that
Connecticut lobstermen fish in New
York State waters. The analysis of other
trap/pot and gillnet vessels applies a
broad assessment of licenses issued by
New York that likely includes licenses
to out-of-state vessels. NMFS
acknowledges that Connecticut-based
vessels that purchase trap tags from
Connecticut may not be accounted for
under Alternatives 2 through 6 Draft (in
the DEIS). However, under the preferred
alternative, Alternative 6 Final, the
portion of waters referred to in this
comment (the ‘‘Race’’) would be
exempted from the proposed regulatory
requirements. As a result, under the
preferred alternative, Connecticut-based
vessels operating in these waters would
not be affected by the regulations. The
EIS acknowledges that fishing activity is
not likely to be equally distributed
throughout state waters. Data on the
location of state-permitted vessel
activity are unavailable; in lieu of better
data, the analysis employs assumptions
that provide a reasonable basis for
estimating the number of affected
vessels. To the extent that fishing
activity is disproportionately
concentrated in waters exempted from
the requirements, fewer vessels than
estimated in the EIS would be affected.
Conversely, to the extent that activity is
disproportionately concentrated outside
of the exempted waters, more vessels
than estimated in the EIS would be
affected.
Comment 80: One commenter wants
LMA 2 to be exempt from any new
regulations as no whales are seen in that
area. Another commenter said that there
is no Dynamic Area Management (DAM)
density in Area 2, thus, the area should
be exempt.
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Response: LMA 2 is located in
Southern New England nearshore
waters, south of Cape Cod and off the
southern coast of Rhode Island. Despite
the fact that a DAM may not have been
triggered in this area, NMFS sightings
data indicate that right whales are
occurring within LMA 2. Although
sightings may not be numerous, right
whales have been seen in these waters,
including areas outside of Long Island
Sound and Block Island. It should also
be noted that DAM zones are a
regulatory measure only intended for
Northern right whales. Thus, a lack in
DAM density is not a reliable indicator
of whale distribution of other species, in
general. Other large whale species
covered under the ALWTRP that would
not trigger a DAM are known to occur
in this area.
Comment 81: One commenter
believed that NMFS does not have a
plan to deal with gear in exempted areas
if and when right whales are reported in
those exempted waters. The commenter
stated that since 2002 it does seem that
there have been a lot more of what is
considered to be out of season/out of
habitat sightings and there is no way for
NMFS to deal with them.
Response: The changes to the
exemption lines have been developed in
response to requests from state fishery
management agencies, as well as others,
and are designed to ensure that the
ALWTRP does not unnecessarily extend
commercial fishing regulations to waters
in which endangered or protected large
whales have been rarely, if ever,
observed and there is low risk. In
developing the revised exempted areas,
NMFS reviewed the available sightings
information (including information
since 2002) and right whale tracking
information where available, and
determined that the potential for
entanglement of whales is low in these
areas so that no changes to the
exemption lines are needed, other than
those modifications noted in this final
rule. NMFS will continue to monitor all
exempted areas, and encourage states to
develop contingency plans in the event
a large whale is sighted in such areas.
Should new information become
available that indicates that a change in
the exemption areas is warranted,
NMFS will share the information with
the ALWTRT and will take appropriate
action.
Comment 82: One commenter
believes that the proposal to exempt
inshore of the 50-fathom (91.4-m or 300ft) curve to explore low profile
groundline is inappropriate. The
commenter states that this proposal
would put whales at risk.
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Response: The alternatives provided
in the DEIS and proposed rule did not
include a proposal to exempt inshore of
the 50-fathom (91.4-m or 300-ft) curve to
explore low profile groundline.
Comment 83: Several commenters
believe that NMFS should analyze the
50-fathom (91.4 m or 300 ft) curve in
Maine as a line for delineating gear
modification requirements (i.e., exempt
inshore of 50 fathoms (91.4 m or 300
ft)). They believe this may protect right
whales going to and from the Bay of
Fundy while allowing operationally
realistic risk reduction gear
modifications.
Response: NMFS sightings data
confirms the frequent occurrence of
right whales in waters landward of the
50-fathom (91.4-m or 300-ft) curve (e.g.,
southern Maine), thus it would not be
an appropriate exemption line.
Comments on Proposed Exemption
Lines in Maine
Comment 84: One commenter said
that if there is going to be an exemption
line set, it should be based off LMA 1,
which already has a line 40 miles (64.4
km) out. The commenter suggested
using this line until research shows a
problem inside the line. The commenter
said the problem is not in the nearshore
fishery where 95-percent of fishermen
in the State of Maine are fishing.
Response: In developing potential
changes to state exempted waters,
NMFS reviewed the NARW Sightings
Database from 1960 through midSeptember 2005 containing dedicated
survey effort and opportunistic sightings
data, which is supplemented by
additional data on humpback and fin
whale sightings, sightings data collected
from 2002 through 2006 through the
NEFSC systematic aerial surveys and
the Northeast U.S. Right Whale SAS, as
well as a large whale sightings database
compiled by Maine DMR, for data on
right, fin, and humpback whale
sightings from 1960 to 2002. The areas
that would be newly exempted from
ALWTRP requirements contained in
this final rule include only those in
which whales are only occasionally
found and are at low risk, as suggested
both by NMFS’ review of the data and
its current understanding of whale
behavior. NMFS does not believe that
regulating the waters that will be
exempted from the ALWTRP would
have a significant benefit to large
whales. The sightings data do not
support exempting state waters out to 40
nautical miles (64.4 km). Exempting this
large of an area from ALWTRP
regulations would likely have a
significant, direct effect on large whales.
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Comment 85: NMFS received
numerous comments in support of using
the Maine DMR’s suggested exemption
line.
Response: After re-examining the
sightings information from the available
data sources noted in the response to
Comment 84 with respect to both
NMFS’ proposed and Maine DMR’s
suggested exemption lines, NMFS
concluded that exempting areas inside
the State of Maine’s suggested
exemption line will provide an adequate
level of protection to endangered large
whales. Thus, the final exemption line
for the state of Maine will use the
coordinates of the exemption line
suggested by Maine DMR.
Comment 86: If NMFS retains the
proposed exempted line, commenters
asked NMFS to consider the exempted
lines in Maine from headland to
headland (e.g., Cape Small to Cape
Elizabeth and Two Lights) rather than
using the COLREGS because this area
would encompass the same bottom type
and fishing patterns. In addition, one
commenter also stated that there is no
exemption proposed for Penobscot Bay.
Response: NMFS agrees with the
commenters’ concerns and will not use
the COLREGS line in Casco Bay; instead
the exemption line will run just outside
Casco Bay by a line connecting a series
of buoys. The location of the exemption
line in Casco Bay is the same as that
suggested by Maine DMR. Moving this
exemption line from the COLREGS line
to the line suggested by Maine DMR will
not have great economic or biological
impacts because there are few affected
vessels and infrequent whale sightings.
For exempting Penobscot Bay, NMFS’
proposed exemption line incorporated
three coordinates from Maine DMR’s
suggested exemption line to exempt the
Penobscot and Blue Hill Bay areas.
These coordinates will remain largely
the same.
Comment 87: Several commenters
suggested that NMFS consider
extending the Maine state exemption
line to the 3-nautical mile (5.6-km) line.
Their reasons include high boating
traffic during the summer resulting in
increased gear loss and the lack of
whale sightings within the 3 nautical
mile (5.6 km) limit.
Response: NMFS believes that the
area exempted under the Maine state
exemption line contained in this final
rule includes a significant portion of the
area identified by the commenters as
high vessel traffic areas. Consequently,
the potential gear loss related to boat
traffic in areas outside of the Maine
exemption line will not have a
significant economic impact to
fishermen or create a significant ghost
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gear problem. As noted in the response
to Comment 85, NMFS reviewed the
available sightings information in
conjunction with both NMFS’ proposed
and Maine DMR’s suggested exemption
lines, and is adopting the latter
exempted line in the final rule. The
available sightings information did not
support extending the Maine state
exemption line to the 3-nautical mile
(5.6-km) line throughout the coast of
Maine.
Comment 88: One commenter thinks
NMFS did not use new satellite tracking
data from Maine and instead relied on
limited sightings data to develop
exempted areas.
Response: The information used by
NMFS to develop and finalize the state
exemption areas was the best scientific
information available. For the final
exemption line, NMFS reviewed the
available sightings database (from 1960
through mid-September 2005), large
whale sightings data from 2002 to 2006
collected through the NEFSC’s
systematic aerial surveys and the SAS,
as well as a large whale sightings
database compiled by Maine DMR, for
data on right, fin, and humpback whale
sightings from 1960 to 2002. NMFS
considered satellite tracking information
that was contained within published
papers to develop and finalize exempted
areas. During the development of the
exempted areas, NMFS considered the
paper entitled, ‘‘Satellite-Monitored
Movements of the Northern Right
Whale’’ (Mate et al., 1997). While
finalizing the exempted areas, NMFS
considered the previous paper in
addition to the paper entitled, ‘‘Summer
and fall habitat of North Atlantic right
whales (Eubalaena glacialis) inferred
from satellite telemetry’’ (Baumgartner
and Mate, 2005). NMFS will continue to
monitor all exempted areas and should
new information become available
regarding the exemption areas, NMFS
will share this information with the
ALWTRT to determine if changes to the
exemption areas are warranted.
Comment 89: Two commenters
questioned the justification of the Maine
exemption line. The commenters
requested NMFS to consider additional
tracking data (one commenter provided
a graphic with the tracking data) based
on two right whale sightings in Maine
waters. One commenter asked NMFS to
see if these whales are landward of the
proposed exemption line. The
commenter stated that documented
movements of two whales in a small
population suggest that Maine waters
are used more frequently than we know;
the other commenter also stated that
entanglement risk still exists when there
is a high concentration of gear and a low
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concentration of whales. Both
commenters stated gear recovered from
the right whales ‘‘Kingfisher’’ and
‘‘Yellowfin’’, with one commenter
noting that ‘‘Kingfisher’s’’ gear came
from Maine.
Response: NMFS will consider
tracking data, and any other new
information that becomes available, and
revisit exemption areas in Maine if
necessary. NMFS considered the
graphic provided by the commenter and
notes that the two whales discussed in
the comments were included in the
Baumgartner and Mate (2005) paper that
NMFS also reviewed. Additionally, as
noted in the Final and Draft EIS, NMFS
did consider published reports of
tracking data (see response to Comment
88). As indicated in Mate et al. (1997),
the accuracy of the whales’ locations
depends on the number and distribution
of the transmissions received from the
tags during a satellite pass. Based on the
number of transmissions received from
the tags during a pass, the locations of
the whales as recorded by the satellite
receivers may vary 150 to 1,000 meters
from the whales’ true locations (Argos,
1990, as found in Mate et al., 1997).
Since the satellite data have levels of
error, precise latitudes and longitudes
are not generated by the tags; thus, it is
difficult to determine exactly where
these whales were sighted with respect
to the final exemption line for Maine.
Although the coordinates for the
sightings were not provided, NMFS did
review the available information and
believes the final exemption line for
Maine is appropriate.
Comment 90: One commenter cited
Exhibit 6–10, which states that 50percent of Maine’s waters would be
exempted under the proposed
exemption line. However, lobster
grounds are only a fraction of state
waters and actual impact upon fishing
effort would be greater and should be
analyzed as such.
Response: The EIS acknowledges that
fishing activity is not likely to be
equally distributed throughout state
waters. Data on the location of statepermitted vessel activity are
unavailable; in lieu of these data, the
analysis employs assumptions that
provide a basis for estimating the
number of affected vessels. To the
extent that actively fished lobster
grounds are disproportionately
concentrated in waters exempted from
the requirements, fewer vessels than
estimated in the EIS would be affected.
Conversely, to the extent that actively
fished lobster grounds are
disproportionately concentrated outside
of the exempted waters, more vessels
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than estimated in the EIS would be
affected.
Comments on Right Whale Critical
Habitat
Comment 91: Due to limitations of
available technology, particularly for
vertical lines, two commenters
recommended that NMFS adopt
seasonal closures to prohibit all gillnet
and lobster gear in all designated right
whale critical habitats during times
when whales are known to congregate
in those areas until gear modifications
that give reasonable assurance to
prevent entanglement are developed.
Two commenters urged NMFS to
consider revising right whale critical
habitat. One commenter suggested
NMFS revise right whale critical habitat
to include both SAM areas as well as the
DAM areas that had been implemented
through 2004. The other commenter
suggested NMFS analyze all available
right whale sightings data to reassess
appropriate critical habitat boundaries
that encompass high-use feeding and
calving habitat.
Response: NMFS did consider
adopting new seasonal closures in
critical habitat areas in response to
comments provided during the scoping
process for the DEIS. This issue was
included in the DEIS summary of
written scoping comments received. The
issue is addressed in the section of the
DEIS that lists the alternatives
considered and rationale for rejection
(e.g., implement a gillnet closure in the
Great South Channel Sliver Area from
April 1 through June 30), as well as in
the section that describes the
alternatives considered (e.g., gillnet
fisheries not currently regulated would
be required to abide by current
restrictions which include closures). In
the FEIS, NMFS included additional
language to clarify that this comment
was considered but rejected.
There are currently closures in place
to protect critical habitat. Contrary to
the sentiments expressed by the
commenters, NMFS is not relieving
current restrictions in critical habitat
areas. This is consistent with the
Conservationist members’ proposal
provided at the 2003 ALWTRT meeting
that, amongst other measures, critical
habitat restrictions remain in place until
vertical and groundline risks are
reduced. In fact, Alternatives 2 through
6 in the DEIS considered that any gillnet
and trap/pot fishery not regulated in
these areas be required to abide by the
current Critical Habitat restrictions (e.g.,
gillnet closure in Cape Cod Bay Critical
Habitat Area from January 1 through
May 15; trap/pot closure in Great South
Channel Critical Habitat Area from
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April 1 through June 30). Additional
closures to fisheries operating in Critical
Habitat areas were not within the scope
of the DEIS.
The preferred alternative in the FEIS
takes a broad-based management
approach by expanding the more
protective gear modifications for lobster
in Cape Cod Bay Critical Habitat, and
lobster and gillnet gear for the DAM gear
modifications coast-wide. Additionally,
as discussed in the FEIS, NMFS believes
that there is a need to re-evaluate
whether critical habitat boundaries
should be modified, and revisit the
relationship between critical habitat and
the ALWTRP before further changing
current requirements in these areas.
NMFS is currently taking a number of
steps prior to deciding whether to
propose any revisions to critical habitat,
including an analysis of the following:
(1) Southeast U.S. right whale
distribution data in relation to
bathymetry and sea surface temperature
derived from Advanced Very High
Resolution Radiometer imagery; and (2)
characterizing the spatial and temporal
distribution of zooplankton in the
Northeast U.S. NMFS hopes to begin
discussions with the ALWTRT
regarding these critical habitat issues
and their relationship to the ALWTRP
in 2008.
Comments on Closed Areas
Comment 92: Several commenters
urged NMFS to continue implementing
closures given the uncertainty of gear
modification effectiveness and until
proven gear modifications are
implemented. One commenter believes
closures are needed for high-risk areas
during peak right whale occurrence (this
is in addition to critical habitat areas)
and suggests removing gear from
feeding/calving areas. In New England,
the commenter suggested closing Cape
Cod Bay to trap/pot fishing during peak
months based on the best available data
at the time (e.g., right whale surveys,
prey abundance). Additionally, the
commenter suggested closures in the
Mid-Atlantic during migration (e.g.,
from the third week of February to the
third week of March and mid-December
to mid-January).
Response: NMFS considered the
concept of a total closure to trap/pot and
gillnet gear in unique ‘‘high risk’’ areas
and determined that gear modifications
developed through the ALWTRT
process would result in more
conservation benefits to the animals.
The basis for this determination is twofold. First, comments received from
some ALWTRT members and the
general public during the scoping and
public hearing meetings stated that
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closures are not an economically
feasible option for commercial
fishermen given the uncertainty of right
whale distribution patterns. Despite
increased aerial survey effort, there is
still a high degree of variability
regarding right whale distribution.
Generally, NMFS has a good
understanding of when and where right
whales will be in an area, but the size
of the area and timing of when right
whales enter these areas vary year to
year. Fishermen could be closed out of
a given area to protect right whales, but
the whales might not yet be in that area.
Similarly, the shift in effort to other
areas may also be to areas where right
whales are present.
Second, total closures refocus fishing
efforts to other areas and may result in
an edge effect where gear is
concentrated around the periphery of a
closed area, posing a greater risk of
entanglement. NMFS believes that the
gear modifications required in this final
rule prevent entanglements where
possible and will alleviate the threat of
serious injury or mortality.
Comment 93: Several commenters
stated that closures may not be very
effective in light of right whale
movements as indicated by satellite
tracking data. Commenters state that
closures may shift gear and effort to the
edges of these areas (i.e., creating a
‘‘wall’’ of gear), thus increasing the
entanglement risk for whales and
placing gear where the whales feed and
travel.
Response: NMFS believes that the
gear modifications required in this final
rule prevent entanglements where
possible and will alleviate the threat of
serious injury or mortality. However, if
future serious injury and mortalities due
to entanglements are proven to have
occurred in high risk areas where gear
modifications are in effect, or in critical
habitat or restricted areas during the
relative restricted periods from
allowable gear, NMFS will consider
closures for reducing the serious injury
and mortality of large whales due to
entanglements by requiring the
complete removal of all trap/pot and/or
gillnet gear. Absent such circumstances,
NMFS will continue to work with the
ALWTRT to monitor and modify fishing
gear to adequately reduce the risk of
serious injury and mortality of large
whales.
Comment 94: One commenter
requested that NMFS analyze the
existing Western Gulf of Maine Closure
that encompasses most of Jeffreys Ledge
for potential inclusion as a year round
modified gear area.
Response: The Western Gulf of Maine
Closure and Jeffreys Ledge area are
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included in ALWTRP management
areas. Modifications to these
management areas were considered in
Alternatives 2, 3, 4, 5, and 6 in the DEIS.
The final rule requires year-round gear
modifications in and around Jeffreys
Ledge. See Chapter 3 section 3.1.7 of the
FEIS or the ‘‘Changes to the ALWTRP
for Gillnet Gear Requirements’’ section
of this preamble for a complete
description of the gear modifications
required for this area.
Comment 95: Several commenters
said that they supported changing the
restricted period for the Southeast U.S.
Restricted Area south of 29°00′ N. lat.
from November 15–March 31 to
December 1–March 31.
Response: Recent data indicate that
right whales are rarely sighted south of
29°00′ N. lat. in November or April.
Consequently, NMFS has determined
that a restricted period beginning on
December 1 and ending on March 31 is
appropriate for the Southeast Restricted
Area N.
Comment 96: One commenter said
that south of 29°00′ N. the area should
be opened due to a lack of whales in the
area. One commenter said that NMFS
should consider an area only 6 miles
(11.1 km) from shore.
Response: Aerial survey and other
sightings data indicate that right whales
routinely move south of 29°00′ N.,
particularly during January and
February. Reviewing sightings data may
suggest most/more whales occur within
a few miles of shore; however, it is
important to note that survey effort is
biased toward shore (see Comment 39)
and thus, whales farther from shore are
likely undercounted.
Comment 97: One commenter
suggested that 26°46.5′ N. should be the
southern boundary for Other Southeast
gillnet waters.
Response: NMFS believes that 27°51′
N. is the appropriate southern boundary
for Southeast Atlantic gillnet fisheries
under the ALWTRP. The line for
operational restrictions is north of
27°51′ N. for both Southeast Atlantic
gillnet and trap/pot fisheries. Right
whales are occasionally found in waters
south of 27°51′ N.; thus, observational
requirements (e.g., VMS, gear marking)
will be in effect under this final rule for
the Southeastern U.S. Atlantic shark
gillnet fishery from 27°51′ N. south to
26°46.5′ N. NMFS will continue to
monitor this area from 27°51′ N. south
to 26°46.5′ N. in the event that sightings
data warrant the expansion of
management areas or restricted time
periods.
Comment 98: One commenter said
that fishing practices south of 29°00′ N.
lat. off Florida are different from those
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north of this line for non-shark gear and
this should be recognized in the
regulations.
Response: NMFS agrees with the
commenter and is aware that the
Southeast U.S. Atlantic shark gillnet
fishery is active primarily south of
29°00′ N. lat. during the restricted
period. Furthermore, NMFS is aware
that the Southeast Atlantic gillnet
fishery has been active north and south
of 29°00′ N. lat. during the restricted
period and that, in general, fishermen
are targeting Spanish mackerel with
runaround nets south of 29°00′ N. lat.
and have used sink gillnets to target
whiting north of 29°00′ N. lat. For this
reason, and due to the seasonal northsouth movements of right whales,
NMFS has divided the Southeast U.S.
Restricted Area into two separate
management areas (N and S) that are
divided at 29°00′ N. lat.
Comment 99: One commenter said
that the restricted period in the
Southeast should be changed from
March 31 to March 25 or earlier south
of the Cape Canaveral and north of
Sebastian Inlet. The commenter also
said that if whales are not present in the
area, it should be opened.
Response: NMFS has considered this
comment. However, sightings data from
aerial surveys indicate that March 31 is
an appropriate temporal boundary for
this area.
Comment 100: One commenter
believed that extending the current
eastern boundary to the EEZ line for
Florida fisheries should only occur if
NMFS has precise data about whale
migratory patterns and routes.
Response: This final rule implements
a broad-based approach to the ALWTRP
regulations, and focuses on the times
and areas where large whales are likely
to occur. NMFS believes that the
boundaries of management areas, as
presented in this final rule, are
appropriate for large whale protection.
Surveys are continually conducted by
the NMFS Southeast Fisheries Science
Center and other NMFS partners. At this
time, NMFS cannot conclude with
certainty that large whales are not
occurring in offshore waters out to the
eastern edge of the EEZ; thus, NMFS
deems it appropriate to extend the
boundary.
Comment 101: Several commenters
suggested that the original names for the
Southeast management areas should be
kept the same for clarity because the
new names are confusing.
Response: Based on public comment,
NMFS is not including the proposed
name change in this final rule. However,
based on the commenters’ view that the
proposed name changes are confusing,
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NMFS is implementing a modified
name change more similar to the status
quo. For regulated waters west of 80°00′
W. long., NMFS is keeping the
‘‘Southeast U.S. Restricted Area’’
terminology and adding a ‘‘N’’ or ‘‘S’’ to
denote North or South of 29°00′ N.
NMFS is changing ‘‘Southeast U.S.
Observer Area’’ to ‘‘Southeast U.S.
Monitoring Area’’ due to the Vessel
Monitoring System (VMS) being
substituted for 100-percent observer
coverage in the Southeastern U.S.
Atlantic shark gillnet fishery.
Comments on SAM and DAM
Comment 102: Several commenters
support the elimination of the SAM
program stating that the effectiveness
and enforceability of SAM is
controversial.
Response: NMFS disagrees with the
commenters’ statements that the SAM
program is being eliminated because of
controversiality regarding its
effectiveness and enforceability. This
final rule implements an expansion of
the SAM program to bridge the gap
between the publication of the final rule
and the effectiveness of the floating
groundline prohibition 12 months after
publication of this final rule. NMFS has
no evidence that the gear modifications
required under the SAM program have
resulted in an entanglement, serious
injury, or mortality to large whales.
NMFS believes that the entanglements
that occurred since the 2002
implementation of the SAM and DAM
programs are the result of gear
interactions with large whales in areas
outside of the SAM and DAM programs.
In fact, this final rule will implement
many of the SAM gear modifications on
a year-round or seasonal basis
throughout the Atlantic coast. The
elimination of the SAM program 12
months after publication of the final
rule is a result of the expansion of the
final SAM gear requirements rather than
an elimination of the SAM program
because it is not effective or enforceable.
NMFS agrees that at-sea enforcement
is important to the success of the
ALWTRP and has conducted
enforcement activities. NMFS also relies
on its partnership with the U.S. Coast
Guard (USCG) and state agencies to
monitor compliance with the ALWTRP.
NMFS has existing penalty schedules
for violations of the MMPA and the
ESA, and regulations pursuant to those
statutes. In addition, NMFS has entered
into agreements with many states to
encourage and facilitate joint
enforcement of regulations. In recent
years, NMFS, in collaboration with the
USCG and its state partners, has targeted
small areas within SAM areas to check
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compliance with SAM gear
modifications. Smaller inshore areas
were chosen based on the volume of
gear fished in the area and the proximity
to right whales. NMFS will continue to
work with its state partners and the
USCG to enforce the requirements of the
ALWTRP.
Comment 103: Many commenters
support maintaining and/or expanding
SAM. The commenters offered the
following suggestions on SAM
expansion: (1) Expanding SAM with
respect to other fishery closures, review
of recent large whale entanglements and
other mortality and foraging data; (2)
expanding SAM requirements yearround; (3) combining an expanded yearround SAM with Alternative 2 to
provide the most conservation benefit to
large whales; and (4) adjusting
expanded SAM boundaries until the
SAM program is eliminated and
replaced with broad-based gear
modifications.
Response: This final rule expands
SAM East and SAM West zones by
increasing the size of the SAM areas
until 12 months after publication of the
final rule when the groundline
requirements are expanded to include
all waters on a year-round or seasonal
basis. Additionally, the boundaries for
the southeast area of SAM East would
be modified. The expanded SAM area
would include the Great South Channel
Critical Habitat area; therefore, trap/pot
and gillnet gear would be subject to the
SAM program inside critical habitat
areas during time periods when the
requirements for fishing inside these
areas are no more conservative than the
surrounding waters (i.e., when the
protections of critical habitat areas
disappear).
Extending SAM to the west and south
will provide greater protection for
endangered whales. Additional analyses
of right whale sightings prompted the
spatial adjustment of SAM West to
better reflect recent data on right whale
seasonal distributions (Merrick, 2005).
Additional broad-scale survey
observations have also been evaluated
by NMFS and support the decision to
expand the SAM area. See Comment
116.
Comment 104: Some commenters
stated that an expanded SAM program
is inadequate. The commenters stated
that it does nothing to protect large
whales in areas outside of SAM areas
and its geographic scale is smaller than
that of whale movements. Furthermore,
one commenter also stated that an
expanded SAM still does nothing to
protect whales going into Cape Cod Bay.
The commenter mentioned it only takes
effect for animals that are leaving Cape
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Cod Bay and the new SAM area will
only include 2 out of the 17 DAM areas.
Response: Extending SAM to the west
and south will provide greater
protection for endangered whales.
Additional analyses of right whale
sightings prompted the spatial
adjustment of SAM West to better reflect
recent data on right whale seasonal
distributions (Merrick, 2005).
Additional broad-scale survey
observations have also been evaluated
by NMFS and support the decision to
expand the SAM area. See Comment
116.
NMFS agrees that relying solely on
the expansion of the SAM program, as
proposed in Alternative 5, is inadequate
to protect large whales for the same
reason stated by the commenter. Except
for the status quo Alternative 1, NMFS
believes that Alternative 5 was the least
conservative, risk-averse approach to
the protection of large whales because it
only required seasonal use of low-risk
gear in the SAM area off the New
England Coast. Although the SAM area
was proposed to be expanded beyond
what is currently required, the use of
low-risk gear would only be required in
a relatively small area along the entire
Atlantic coast at a time when right
whales are known to aggregate. NMFS
believes that Alternative 5 does not
consider seasonal migration patterns of
large whales from Maine to Florida,
resulting in lower risk reduction
compared to both the time and area
requirements provided in NMFS’
approved alternative. Alternative 6
Final uses an expansion of the SAM
program to serve as a bridge to allow
fishermen until 12 months after
publication of the final rule to convert
their groundlines to sinking line. Once
fully converted, the gear modifications
provided under the revised SAM
program will be expanded to include all
New England waters on a year-round
basis and seasonally for the remainder
of the Atlantic coast.
Comment 105: One commenter
disagrees with the 6-month delay in
effective date for SAM. The commenter
states that fishermen using this area
should already have sinking groundline.
Response: NMFS disagrees with the
commenter. This final rule will expand
the current SAM area, which will affect
fishermen who had not been required to
comply with the SAM gear requirements
in the past. The 6-month delay in the
effective date for SAM gear
requirements is to allow fishermen in
the new expanded areas to convert their
gear.
Comment 106: One commenter
opposes regulations in the area
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surrounding Mount Desert Rock, which
could be included in a future SAM plan.
Response: This final rule will expand
the SAM area, which will require gear
modifications during certain times of
the year within these areas. The
expanded SAM requirement will be in
effect until 12 months after publication
of the final rule. The SAM area will not
affect the immediate Mount Desert Rock
area. However, beginning 12 months
after publication of the final rule,
fishermen in the Mount Desert Island
area may be affected by the groundline
requirements, consistent with the SAM
program, depending on whether the
fishermen fish seaward of the Maine
state exemption line.
Comment 107: One commenter
believes that the success of the revised
SAM program, exemption lines, or any
other boundary-based management
approach rests on the assumption that
NMFS sets the boundaries in the most
appropriate locations, considering the
risks to whales and the compliance
costs to fishermen. The commenter
suggested that NMFS work with Maine
DMR to periodically review and adjust
the boundaries and gear requirements of
SAM as necessary.
Response: NMFS agrees with the
commenter. Regarding the SAM
program, NMFS reviewed the NARW
Sightings Database through early 2003,
supplemented by additional data on
humpback and fin whale sightings. In
addition, NMFS used information,
including that which was provided by
the State of Maine, to modify the Maine
state exemption line (see response to
Comment 84). NMFS will continue to
work with Maine, other state partners,
and ALWTRT members to develop
appropriate measures for the ALWTRP.
Comment 108: One commenter
believes the boundaries for expanded
SAM areas do not reduce risk, stating
that the SAM West area does not protect
late winter arrivals (December–
February) and that the overlap is too
small. The commenter states that the
reduced eastern portion of SAM East
combined with DAM elimination equals
a net loss of right whale protection. The
commenter stated that two analyses of
data to determine boundaries for SAM
were March to May and March to July,
but that January and February were not
considered in the analyses. The
commenter stated that sightings data
from 2004–2005 were ignored and
NMFS should have used them (see
https://whale.wheelock.edu/whalenetstuff/reportsRW_NE).
Response: NMFS believes that the
expanded SAM area implemented in
this final rule provides increased
protection for right whales, as well as
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other large whales, in the Gulf of Maine.
NMFS delineated the expanded SAM
area based upon the best data available
at the time, which included data from
approximately 1960 through 2003 from
the NARW database distributed in
December 2004 (Merrick 2005). This
dataset included sightings through fall
2003; the 2004 data had not been added
and the 2005 data had not yet been
collected. NMFS analyzed data from
March through July only, and did not
analyze data from January and February
as there were very little winter sighting
data available at that time.
Comment 109: NMFS received
numerous comments supporting the
elimination of the DAM program.
Response: This final rule eliminates
the DAM program six months after
publication of this final rule.
Comment 110: Two commenters
supported elimination of the DAM
program but were concerned that it will
reduce the incentive for fishermen to
change over their gear. Another
commenter stated that the
unpredictability of the DAM program
can lead to fishermen converting their
gear.
Response: NMFS believes that
eliminating the DAM program will not
reduce the incentive for commercial
fishermen to convert to the SAM or
DAM gear modifications. When the
initial SAM and DAM programs were
implemented in 2002 and the DAM
program was amended in 2003, NMFS
acknowledged that one of the benefits of
these programs was that they provided
an incentive for commercial fishermen
to convert their gear to the more
restrictive gear requirements on a yearround basis. NMFS believes that many
fishermen chose to convert on a yearround basis to avoid interruptions in
their fishing seasons because of gear
modifications imposed by the SAM and
DAM programs. Furthermore, two gear
buyback programs have been completed,
and a third buyback program is
currently underway. These buyback
programs provide more incentive to
fishermen to convert their gear because
they are compensated for converting
their gear prior to the implementation of
the more restrictive gear requirements.
Comment 111: Many commenters
believe that the DAM program should
not be eliminated 6 months after
publication of this final rule and NMFS
should keep the DAM program as part
of the ALWTRP. The commenters
believe that if NMFS eliminates DAM,
there is no contingency measure for
when whales are sighted in exempted
areas. Specifically, some commenters
said there will be no method to protect
right whale aggregations in the Gulf of
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Maine (outside SAM) between now and
2008, especially during the fall and
winter.
Response: The DAM program is not
designed for exempted areas. This final
rule expands the SAM area and allows
the DAM program to be eliminated six
months after publication of this final
rule. NMFS conducted two different
analyses to examine whether and where
SAM would provide additional
protection to right whales. The results of
these analyses indicated that the area to
be incorporated into the expanded SAM
would encompass many of the areas that
previously have been designated as
DAM areas. Thus, NMFS believes that
replacement of the DAM program with
an expanded SAM program will
increase the protection afforded to
whales. In addition, NMFS believes that
expanding the SAM area will provide
greater protection to right whales in the
Northeast during times of predictable
spring aggregations. In particular, the
new overlap of SAM East and SAM
West will provide a direct benefit to
right whales in this area during April,
when the number of right whales in the
vicinity is expected to be high. In
addition, six months after publication of
this final rule, additional gear
modifications will take effect in the
areas outside of the expanded SAM
area.
Comment 112: Some commenters
supported eliminating the DAM
program as soon as sinking/neutrally
buoyant groundline requirements take
effect (e.g., 2009 in some areas and 2010
in others). Several commenters favored
elimination of the DAM program, but
support its continuation until 2008 or
2009 with the implementation of gear
modifications (e.g., low profile
groundline). Other commenters believed
the DAM program should be eliminated
as soon as possible with the SAM
expansion.
Response: See response to Comment
111. As described in the DEIS, NMFS
considered but rejected the low profile
groundline concept (see also Response
to Comment 158).
Comment 113: Two commenters
encouraged NMFS to retain and expand
the DAM program into the Mid-Atlantic
area even though they believe it takes
NMFS too long to implement; the
commenters suggested speeding up the
process of filing the DAM rules in the
Federal Register. Another commenter
said that DAMs should be implemented
and rescinded more quickly.
Response: NMFS explored options to
expedite the implementation of DAM
areas. Once a DAM area is identified,
NMFS must determine the appropriate
action by considering a variety of
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factors, including but not limited to: the
location of the DAM zone with respect
to other fishery closure areas, weather
conditions as they relate to the safety of
human life at sea, the type and amount
of gear already present in the area, and
a review of recent right whale
entanglement and mortality data.
Despite NMFS best efforts to expedite
the analysis of these factors, it still takes
some time to complete and review the
analysis prior to approval and
implementation. Given the decision
factors for implementing restrictions
within a DAM area and the time needed
to complete and review the analysis,
NMFS could not find any ways to
expedite the process. NMFS believes
that replacing the DAM program with
broad-based gear modifications
designed to reduce entanglements and
serious injury should an entanglement
occur will increase the protection of
right whales.
Comment 114: One commenter
recommended expanding closed areas to
buffer DAM zones and to allow for
unpredictable movements of individual
whales.
Response: The ALWTRP regulations
favor broad-based gear modifications
over area closures. Movement and
location of whales is often difficult to
predict with certainty, making gear
modifications more protective than
closures of limited areas. Furthermore,
closures may produce undesirable
consequences such as concentrations of
gear just outside of closed areas, which
could increase entanglement risks to
large whales.
Comment 115: Several commenters
encouraged NMFS to increase
enforcement of DAMs and one
commenter supported removing all gear
from DAM zones to ease enforcement. If
this does not occur, the commenter
encouraged NMFS to develop a more
effective enforcement strategy.
Response: The decision to eliminate
the DAM program is not based on
enforcement issues. NMFS has
developed and implements a successful
enforcement strategy for the DAM
program through its agreements with its
state partners and the vessel and aerial
support provided by the USCG.
Comment 116: Some commenters
suggested the agency should include all
previous DAM zones into an expanded
SAM, up to and including trigger areas
defined by NMFS in 2005. Further,
these commenters presume that NMFS
believes expanded SAM would cover
high use areas most likely to pose risk
outside of critical habitat areas, such as
Jeffreys Ledge, Stellwagen Bank, and the
waters east of Chatham, MA. One
commenter requested that NMFS revisit
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the expanded SAM analysis for
Alternative 2, given that several DAM
zones occurred outside the expanded
SAM area from 2003–2005.
Response: NMFS considered many
DAM areas when expanding SAM
boundaries for this final rule. If whales
were observed in the same area during
the same season in three or more years,
then this area was considered to have
predictable concentrations of whales,
and was incorporated into the final
SAM area. However, many DAMs only
occurred once in an area and were thus
considered too unpredictable to be
considered as Seasonal Management
zones (Merrick 2005). Beginning 12
months after publication of this final
rule, the expanded SAM zones will be
eliminated as the final gear
modifications required in the SAM
zones will be expanded to include all
areas, both spatially and temporarily,
throughout the range of right whales
and other large whale species.
Comments on Effective Date
Comment 117: Many commenters
urged NMFS to implement gear
modifications sooner than 2008. The
commenters believed NMFS should
implement ALWTRP modifications
sooner because: (1) The proposed
effective date does not comply with the
MMPA; (2) the proposed effective date
does not comply with the intent of ESA;
and (3) PBR is being exceeded. Several
commenters believed the gear
modifications should occur sooner than
2008 in certain large whale habitats,
such as Great South Channel,
Stellwagen Bank, and Jeffreys Ledge,
especially in light of the Massachusetts
buyback program that assisted
fishermen in converting to sinking and/
or neutrally buoyant groundline.
Response: The ESA requires agency
actions to avoid jeopardy, and NMFS
believes the effective dates for this
action are sufficient to avoid jeopardy.
The action and effective dates are also
in compliance with the goals of the
MMPA, including reducing serious
injury and mortality of large whales to
below PBR.
In 2004, the International Fund for
Animal Welfare, Massachusetts Division
of Marine Fisheries (MADMF), and the
Massachusetts Lobstermen’s Association
partnered to implement a lobster gear
buyback program. More than $650,000
was disbursed to Massachusetts lobster
fishermen who turned in floating
groundline; these fishermen replaced
the floating line with non-buoyant line
consistent with the measures contained
in this final rule. Therefore, NMFS
believes a portion of the industry is
voluntarily implementing the measures
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in this final rule before they are required
to do so through the ALWTRP. In
addition, NMFS, in collaboration with
National Fish and Wildlife Foundation
(NFWF), administered a similar buyback
program in the Mid-Atlantic; see
response to Comment 110. Finally, the
Gulf of Maine Lobster Foundation
received a grant from NMFS for the
development and implementation of a
floating groundline buyback and
recycling program, in which floating
groundline is exchanged for sinking or
neutrally buoyant groundline. The first
phase of this program took place in May
2007 in southern Maine and
participants included Maine state
lobster fishermen in Zone G as well as
federal lobster permit holders in Maine.
Comment 118: Many commenters
stated that the time period for
implementing the final rule is too short.
The commenters believe NMFS should
extend the time to implement the
ALWTRP because: (1) There is a limited
availability of line; (2) price gouging
may occur; (3) gear manufacturers are
hesitant to produce line based on their
awareness of current line testing; (4)
there is a lack of awareness of the actual
[line] breaking strength and schedule of
degradation; (5) there is no immediate
process for changing line; (6) two line
testing experiments are currently
underway to determine the usable life of
sinking groundline and the practical
commercial application of new
materials; (7) it will give offshore
lobstermen more time and allow NMFS
to consider the possibility of low profile
groundline; (8) it will allow for more
research and financial planning by
industry; (9) as is, it would cause a large
capital expenditure over a 2-year period;
(10) it will give the Federal Government
and environmental groups more time
needed to secure funding to minimize
the financial burden; and (11) it will
cost approximately $100,000 for an
offshore lobsterman to switch over his
gear. Many commenters suggested an
implementation time of 4 years from the
publication date of the final rule.
Response: Typically, NMFS provides
30 or 60 days for fishermen to comply
with gear modifications such as mesh
size restrictions and other requirements.
However, as evident by overwhelming
public comment, given the magnitude of
the time and resources needed by
fishermen to change their gear to
sinking and/or neutrally buoyant
groundline requirement, NMFS believes
giving fishermen 12 months from the
publication of the final rule to comply
is warranted. See the ‘‘Comments on
Low Profile’’ portion of the this section
with respect to low profile issues. The
costs and impacts analyzed in Chapters
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6 and 7 of the EIS explicitly consider
the incremental effects of groundline
replacement beyond routine levels. The
cost analysis presented in the EIS is
based on prevailing market prices for all
factor inputs, including neutrally
buoyant and/or sinking groundline. One
commenter points out that groundline
suppliers may take advantage of a
mandate to use neutrally buoyant and/
or sinking groundline by resorting to
price gouging, i.e., charging artificially
high prices in order to realize large
profits. The government is aware of the
potential for such behavior and, if it
occurs, may take action to stop it. NMFS
also believes, however, that the
schedule for implementing the
modifications in the final rule will
reduce the potential for price gouging.
The requirement to use neutrally
buoyant and/or sinking groundline does
not take effect until 12 months after
publication of the final rule. NMFS
believes spreading initial demand for
neutrally buoyant and/or sinking line
over this period of time will likely
relieve market pressures that might
otherwise lead to price gouging. NMFS
further believes the 12 month phase-in
period would give suppliers of neutrally
buoyant and/or sinking line the
opportunity to increase production to
meet the increased demand; this
increase in production would likely
mitigate against price gouging. Thus,
NMFS believes rope will continue to be
available for fishermen to comply with
the effective date for the ALWTRP
sinking and/or neutrally buoyant
groundline requirements.
Although the model vessels analyzed
in Chapter 6 of the EIS are generalized
and may not reflect costs for all
individual vessels, NMFS does not
believe incremental costs (i.e., costs
beyond routine gear replacement costs)
will typically be as high as $100,000.
The analysis suggests that initial
investment costs are more on the order
of $39,000 for large offshore vessels.
Furthermore, while costs may be high
for some large offshore lobster vessels,
the compliance costs are generally
commensurate with revenues for these
large operations, i.e., costs as a percent
of revenue are not prohibitive. Chapter
7 of the EIS identifies vessel segments
that may be heavily impacted by the
requirements and suggests that under
Alternative 6 Final (Preferred), a limited
number of small vessels are most at risk.
Although costs are high for some
vessels, NMFS made modifications to
the final rule, based on public comment,
to decrease costs where possible while
still meeting its goals under the MMPA
and ESA (see Changes from the
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Proposed Rule section of the preamble).
While these vessels may still realize
high costs relative to revenues,
fishermen have some options to try to
mitigate the costs. For example, the
impacts of converting to sinking and/or
neutrally buoyant groundline may be
defrayed, in part, by current and future
groundline buyback programs operated
by NMFS and other partners. In
addition, although the requirements
under Alternative 6 Final (Preferred)
may impose significant costs within the
first year after publication of the final
rule (to convert all groundline to sinking
and/or neutrally buoyant groundline),
fishermen may be able to distribute the
cost of the new gear over its useful life
by seeking a loan. After the first year,
ongoing costs would be significantly
lower as fishermen would only need to
replace worn-out and lost gear.
Comment 119: One commenter
suggested NMFS require switching to
sinking/neutrally buoyant groundline
for trap/pot gear in 2009.
Response: The sinking and/or
neutrally buoyant groundline
requirement will be effective in
expanded SAM areas six months after
publication of this final rule, and in all
other areas effective 12 months after
publication.
Comment 120: Some commenters
stated that complying with the proposed
weak link regulations by 2008 would be
problematic. One commenter stated that
splicing weak links into existing gear
will be time-consuming, costly, change
how gillnets work, and lower the catch.
The commenters suggested requiring
weak links by 2009 or 2010, as this
would help reduce compliance costs
and allow more time for gear
modification.
Response: NMFS agrees that meeting
the increase in the number of weak links
per net panel from one to five or more,
depending on the length of the net
panel, will take time for fishermen.
However, based on public comments
received, this final rule gives gillnet
fishermen 2 options to install the
additional net panel weak links. These
two net panel weak link options will be
effective six months after publication of
the final rule. However, thirty days after
publication of the final rule, these net
panel weak link options will be allowed
in current SAM areas and implemented
DAM zones when a gear modification
option is selected.
Comment 121: One commenter states
that NMFS seems to be balancing
interests of different groups that
advocate for accelerated phase-in of gear
modifications with those that favor a
longer phase-in period. The commenter
stated that NMFS sees species survival
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equal to the interests of the fishing
industry, and that this approach directly
counters NMFS’ obligation to protect
whales and take measures to recover
species under the MMPA and ESA.
Response: NMFS disagrees and
believes it is implementing the
appropriate measures to reduce risk
associated with groundlines, amongst
other risk reduction measures, as
quickly as is feasible and consistent
with the requirements of the MMPA and
ESA.
Comments on Groundline
Comment 122: One commenter
questioned whether there is
overwhelming evidence that groundline
has caused entanglements.
Response: There is evidence that
groundline has been involved in whale
entanglements. Both buoy lines and
groundlines have been identified as
sources of entanglements.
Comment 123: Many commenters
supported the use of sinking groundline.
One commenter stated that it will
substantially reduce entanglement risks
because it will reduce the amount of
line in the water column. One
commenter stated there are few areas in
Massachusetts where large whales have
not been sighted, and also stated that
sinking groundline may cause fewer
gear conflicts. However, another
commenter supported the use of sinking
groundline only if it would help the
whales, and is not in favor of it in areas
where there are going to be gear losses
and it would not save any whales.
Response: NMFS appreciates the
support with respect to sinking and/or
neutrally buoyant groundline and agrees
that the end result is less line in the
water column, and therefore a reduced
risk of entanglement. NMFS agrees that
fewer gear conflicts may be a byproduct
of sinking and/or neutrally buoyant
groundline. As discussed in the FEIS,
NMFS believes the use of sinking
groundline will reduce the risk of
entanglement and recognizes it may
increase gear losses.
Comment 124: One commenter
cautions that juvenile humpback whales
and right whales have emerged with
mud on their heads, which indicates
feeding on the bottom. Therefore, risks
to these whales may be increased when
using sinking groundline. The
commenter states that it will be critical
to monitor gear modifications,
specifically regarding how and when
effectiveness will be measured.
Response: Although there are
anecdotal reports of whales going to the
bottom or having scratches on their
snouts and stomachs, presumably from
traveling to the bottom, there is little
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published data that supports these
reports; whale behavior (i.e., foraging) at
various depths and bottom types is also
largely unknown at this time. NMFS
recognizes that whales may spend time
at or near the bottom in some habitats,
as described by the commenter. The
sinking groundline concept is a measure
to remove the maximum amount of line
from the water column in an effort to
reduce the overall risk of entanglement.
See also Comment 267.
Comment 125: Many commenters
believed that rocky ledges are unlikely
habitat for large whales and questioned
whether NMFS knew if large whales are
bottom feeders around rocky bottoms.
These commenters also believed low
profile line should not be prohibited in
such areas (i.e., inshore rocky habitat).
Response: Currently, available data
and scientific literature do not suggest
that whales treat rocky bottom areas any
differently than locations with other
bottom types (e.g., mud). NMFS data
show whales aggregate over the
northern edges of George’s Bank, which
is dominated by rocky ledges. NMFS
acknowledges that a better
understanding is needed on prey
distribution, and how whales utilize the
water column, including the foraging
and diving behavior of whales.
Comment 126: One commenter does
not believe that sinking/neutrally
buoyant groundline would pose a risk to
bottom-feeding whales.
Response: NMFS recognizes that any
line in the ocean poses some risk of
entanglement and believes that sinking
and/or neutrally buoyant line reduces
that risk substantially.
Comment 127: One commenter
supports sinking groundline for gillnet
gear.
Response: NMFS appreciates the
support for sinking groundline in gillnet
gear.
Comment 128: Many commenters
opposed sinking/neutrally buoyant
groundline. The commenters objected to
this requirement because they believed
the use of sinking/neutrally buoyant
groundline would cause the following:
(1) The potential for an increase in
hangdowns, chafe, snag and/or burring
that would then increase gear loss/ghost
gear; (2) safety issues and potential
injury to fishermen; (3) a significant
increase of vertical lines in the water as
fishermen who normally fish pairs,
triples, or trawls would probably move
to fishing singles (i.e., if they had to use
sinking and/or neutrally buoyant line);
(4) the line to twist around the traps;
and (5) the line to sand up during
storms and making it hard to grapple to
get it back. Furthermore, commenters
cited other reasoning for not using
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sinking/neutrally buoyant groundline,
including: (1) The threat to large whales
is not reduced by changing line type
(Johnson et al., 2005); (2) replacement
costs for traps (traps cost $55 to $70)
and line would be expensive; (3) the
rope manufacturers could not produce
enough line to outfit the offshore fleet
by 2008; and (4) switching away from
floating line will force everyone to fish
in the gravel and mud gullies, instead of
the hard bottom, and will increase
congestion.
Response: The fishing industry from
Maine to Florida utilized sinking line
successfully in a variety of applications
prior to the advent of floating line, and
some percentage of fishermen today do
not use floating groundline for a variety
of reasons. In implementing a
prohibition on floating groundline,
NMFS acknowledges fishermen may
experience operational difficulties in
adjusting to sinking and/or neutrally
buoyant groundline in different habitats.
However, NMFS believes that industry
can develop fishing practices to address
any difficulties in transitioning from
floating groundline to sinking and/or
neutrally buoyant groundline, as
evident at the 2005 NMFS Low Profile
Groundline Workshops by one
fishermen transitioning in rocky habitat
areas. NMFS further acknowledges that
the potential for hangdowns and gear
loss/ghost gear may increase. The
economic cost analysis in the FEIS
explicitly takes into account potential
changes in gear loss rates under the
various regulatory alternatives. The
economic analysis also explicitly takes
into account the need to replace sinking
and/or neutrally buoyant line more
frequently than floating line.
NMFS believes that the gear
modifications required under the
ALWTRP do not present any significant
increased dangers above those of normal
fishing practices. However, NMFS will
continue to monitor this situation
through discussions with industry and
the ALWTRT.
NMFS recognizes there may be an
increase of vertical lines due to the
number of traps per trawl being
reduced; however, the total amount of
line in the water column will be
reduced as a result of the neutrally
buoyant line measures. There are
currently provisions in the regulations
that prohibit single traps in certain
times and areas to reduce the overall
number of vertical lines. NMFS believes
the reduction of line in the water
column based on the use of sinking and/
or neutrally buoyant groundline will
provide a substantial reduction in
entanglement risk. NMFS also
recognizes the issue of vertical lines as
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an entanglement risk and will be
addressing that subject with the
ALWTRT. NMFS recognizes the
potential for groundline to twist around
traps and that this may contribute to
hangdowns; however, the risk reduction
associated with the use of sinking and/
or neutrally buoyant groundline
warrants this gear configuration. NMFS
recognizes that the longevity of sinking
and/or neutrally buoyant groundline has
the potential for being less than floating
groundline. NMFS believes that the rope
manufacturing industry is aware of the
issue and will continue to work on
enhanced lines that address this
concern.
NMFS believes that using sinking
and/or neutrally buoyant groundline, as
opposed to floating groundline, will
reduce risk of entanglement. The is also
supported by a study by Johnson et al.
(2005).
NMFS recognizes there are costs to
the fishing industry to comply with
these gear provisions. Groundline
replacement costs represent a large
share of the overall compliance costs for
most affected vessels. The social impact
analysis included in the FEIS examines
the economic burden posed by the
alternatives and the likely effect on the
economic viability of fishing operations.
The analysis identifies vessel segments
that may be heavily impacted by the
requirements and suggests that under
Alternative 6 Final (Preferred) a limited
number of small vessels are most at risk
when comparing annual compliance
costs to average per-vessel revenues.
While some of these small vessels face
costs that could potentially drive them
out of business, current and future
groundline buyback programs may help
defray the compliance costs for many
vessels. See response to Comment 57 for
additional information related to
defraying costs.
NMFS and its state partners have
worked with rope manufacturers to keep
that industry informed of the potential
for a large increase in demand for
sinking and/or neutrally buoyant line.
In addition, the requirements are spread
over a one year period.
NMFS recognizes that the change
from floating groundline to sinking or
neutrally buoyant groundline may result
in changes in fishing practices and
areas. The risk reduction warrants these
changes in fishing practices and gear
configuration.
Comment 129: One commenter stated
that the $120,000 cost that fishermen are
expecting/predicting does not take into
account petroleum, the rising cost of
everything, or the fact that sinking rope
is heavier than the floating rope that is
being used. The Commenter states that
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fishermen will have to replace their
rope more and more, which is double or
triple the cost of what they are currently
spending. This will result in price
gouging.
Response: While the model vessels
employed in the economic impact
analysis presented in the EIS are
generalized and may not reflect costs for
all individual vessels, NMFS does not
believe incremental costs (i.e., costs
beyond routine gear replacement costs)
will typically be as high as $120,000.
The analysis suggests that initial
investment costs are likely to be more
on the order of $39,000 for large
offshore vessels. While it is true that
input costs—particularly fuel costs—are
rising, the cost analysis presented in the
FEIS has been updated to reflect recent
changes in costs. The price of sinking
and/or neutrally buoyant line employed
in the analysis is greater than the price
it specifies for floating line, but the
difference is less than a factor of two
(not the two to three factor noted by the
commenter). In addition, the cost
analysis incorporates assumptions that
recognize the shorter useful life of
sinking and/or neutrally buoyant
groundline. Regarding price gouging,
the government is aware of the potential
for such behavior and, if it occurs, may
take action to stop it. NMFS also
believes that the schedule for
implementing the modifications in this
final rule will reduce the potential for
price gouging. The requirement to use
sinking and/or neutrally buoyant
groundline does not take effect until 12
months after publication of the final
rule. NMFS believes spreading initial
demand for sinking and/or neutrally
buoyant groundline over this period of
time will likely relieve market pressures
that might otherwise lead to price
gouging. NMFS further believes the 12
month phase-in period would give
suppliers of sinking and/or neutrally
buoyant groundline time to increase
production to meet the increase in
demand; this increase in production
would likely mitigate against price
gouging. See also Comment 118.
Comment 130: Several commenters
questioned the quality and durability of
sinking groundline, stating that
fishermen cannot find anything that
lasts more than 2 years, whereas 15-year
old float rope is as good as new. Other
commenters believed that more research
should be conducted to make sinking
rope more durable before any
regulations require the use of sinking
line. They stated that sinking line frays
more easily in the normal course of
fishing and consequently wears out
faster than polyester and polyurethane
floating rope and it is more expensive.
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Response: Sinking groundline has
been utilized in the fishing industry for
many years and new line blends have
been and continue to be developed to
address the issues raised in this
comment. NMFS has funded research
with the states, manufacturers, and
industry to address this issue. Based on
public comment received, industry and
state fishery management
representatives noted that in some
unique areas, particularly off the coast
of Maine, there may be a need to allow
groundline the ability to float over rocky
bottom types. See response to Comment
158 on issues related to ‘‘low profile’’
groundline.
Comment 131: Commenters stated
that, in New Jersey, groundlines are
usually full of recreational fishing
hooks. The commenters believe sinking
rope is not durable enough to handle
pulling hooks out often, so they will
have to replace sinking groundline more
often than floating groundline.
Response: This issue appears to be
unique to New Jersey and may require
that the affected fisherman work with
line manufacturers to develop an
enhanced sinking groundline to address
this issue. NMFS believes that sinking
and/or neutrally buoyant groundline
may actually reduce the incidence of
recreational hook entanglement in
groundlines as the groundline will be
out of the water column, therefore less
likely to encounter the recreational gear,
as recreational hooks travel up and
down through the water column.
Comment 132: Several commenters
believe that fishing with sinking and/or
neutrally buoyant line will cause
‘‘hangdowns’’ to occur every few
minutes, which will increase abrasion
and cause the line to fill with sand.
Furthermore, hangdowns are considered
a safety hazard. For example, a USCG
Safety Alert issued on May 28, 1998, for
small vessel stability warned that ‘‘gear
hung down on the seabed’’ is a
dangerous condition to fishermen; even
larger vessels up to 50 ft (15.2 m) will
be at severe safety risk due to rope
getting stuck under rocks/ledges.
Response: See Response to Comment
128.
Comment 133: Several commenters
stated that there are many areas where
sinking and/or neutrally buoyant
groundline cannot be used; instead they
should be allowed to use float rope in
those areas. Many commenters referred
to hard/rocky/tidal/ragged bottoms and/
or habitats. Commenters suggested that
sinking and or neutrally buoyant line is
not feasible in these areas because: (1)
There would be a large amount of gear
loss if required to use sinking line; (2)
there would be chafing; (3) there would
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be an increase in hangdowns; and (4) it
is impossible to fish the hard bottom in
Maine using pairs, triples, or trawls
without the use of floating groundline.
Other areas where commenters stated
sinking and/or neutrally buoyant line
could not be used included: (1)
Downeast Maine (one commenter made
a specific reference to bottom
topography changes east of Casco Bay);
(2) the North Carolina black sea bass
fishery; (3) live rock or coral areas; (4)
wrecks; (5) reefs; and (6) bottoms that
include sand and shell (clam and
oyster), as it would could cause chafing.
Response: See Response to Comment
128 regarding hangdowns, chafing,
unique bottom types and bottom
compositions. See below for habitat and
coral area discussion.
NMFS acknowledges there are unique
issues related to habitat impacts, live
rock and coral areas and, although
sinking and/or neutrally buoyant
groundlines could interact with the
seafloor and adversely impact benthic
marine habitats, these impacts are not
expected to be more than minimal when
compared to the use of floating
groundline. The FEIS provides a
description of the affected environment,
including the identification of areas
designated as Essential Fish Habitat
(EFH) and Habitat Areas of Particular
Concern (HAPCs) as well as an analysis
of the impacts of fishing gear on this
environment. Bottom-tending static gear
(e.g., traps/pots) has been found to have
low to moderate effects on benthic
habitats when compared to the more
severe physical and biological impacts
caused by bottom-tending mobile gear
(e.g., bottom trawls and dredges).
Furthermore, the amount of bottom area
that would be disturbed by sinking and/
or neutrally buoyant groundline, and
the frequency of disturbance in the
exact same area that would result from
repeated contact with sinking and/or
neutrally buoyant groundline, would be
very small, allowing enough time for
recovery of benthic communities that
would potentially be affected. Thus,
NMFS has concluded that the final
preferred alternative is not expected to
have more than a minimal and
temporary adverse impact on benthic
EFH.
NMFS evaluates and regulates the
adverse impacts of fishing on bottom
habitats in other management actions.
Currently, several areas in the Northeast
(e.g., on Georges Bank, in southern New
England, and in the Gulf of Maine) are
closed to the use of mobile, bottomtending fishing gear, such as bottom
trawls and dredges, and two offshore
canyons (e.g., Lydonia and
Oceanographer) are closed to the use of
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bottom trawls and gillnets by vessels
using monkfish days-at-sea permits. The
monkfish closures have the added
benefit of protecting deep-water corals
and other structure-forming organisms
in these two canyons. The New England
Fishery Management Council (NEFMC)
published a Notice of Intent on February
24, 2004 (69 FR 8367), to prepare a
programmatic EIS and Omnibus EFH
Amendment that will apply to all
Council-managed FMPs. This
amendment has been divided into two
phases (70 FR 53636, September 9,
2005). In phase 1, the amendment will
revise the existing EFH and HAPC
designations for all 27 Council-managed
species. In phase 2, the NEFMC is
expected to identify and implement new
measures to minimize the adverse
impacts of fishing on EFH, which would
replace or supplement the existing
regulations. Final action on the
Omnibus Amendment is not expected
until late 2008 or early 2009. EFH
protection measures are also being
considered by the Mid-Atlantic Fishery
Management Council in individual
FMPs that will be promulgated during
the next several years. The Atlantic
States Marine Fisheries Commission
(ASFMC), composed of representatives
from the Atlantic coastal states and the
Federal Government, develops fishery
conservation and management strategies
for certain coastal species, including
American lobster, and coordinates the
efforts of the states and the Federal
Government toward concerted
sustainable ends. NMFS is working
cooperatively with the ASFMC to
evaluate the EFH impacts of the lobster
trap fishery. In the Southeast, with
regard to preventing, mitigating, and
minimizing the adverse effects of fishing
on EFH, the Gulf of Mexico and
Caribbean Fishery Management
Councils (FMC) in 2004 considered
prohibiting sinking groundlines
between traps/pots traps to prevent
sweeping of the bottom during trap/pot
retrieval and recognized the effect of
probable increased interactions of buoy
gear with marine mammals by requiring
individually buoyed traps/pots. In 1991,
the South Atlantic FMC prohibited fish
traps throughout its jurisdiction with
the exception of black sea bass pots
north of Cape Canaveral, Florida,
because sea bass pots are small, fished
primarily in shallow waters less than 20
fathoms (36.9 m or 120 ft), and there
was a lack of evidence of environmental
harm. This Council is currently
conducting a review of its EFH
designations and provisions to protect
EFH. Each of the southeast Councils
identified practicable measures to
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minimize adverse effects of fishing by
using a variety of factors when
evaluating the impacts of fishing gears.
These included the duration and
frequency of the impact, the intensity
and spatial extent of the impact, and the
sensitivity of the habitat and habitat
functions. When considering these
factors and that the proposed action will
not change fishing practices, NMFS
believes that sinking and/or neutrally
buoyant groundlines would result in
impacts on EFH that would be no more
than minimal and temporary in nature.
Additionally, in response to a petition
by Oceana to immediately promulgate a
rule to protect deep-sea coral and
sponge (DSCS) habitat from the impacts
of mobile bottom-tending fishing gear,
NMFS outlined an approach to address
these issues (70 FR 39700, July 11,
2005). Specifically, NMFS adopted an
approach to address DSCS issues that
will be formalized in a National DSCS
Conservation and Management Strategy.
NMFS will work actively with each
Regional FMC and the ASMFC to
evaluate the issue, and take action
where appropriate, to protect DSCS,
which may include future rulemaking to
protect DSCS in specific locations based
on analyses for specific fisheries.
Additionally, NMFS plans to develop a
strategy to address research,
conservation, and management issues
regarding DSCS habitat, which
eventually may result in rulemaking for
some fisheries.
Comment 134: Many commenters
believe that sinking line should not be
required more than 100 miles (185.2
km) offshore or in deep canyons.
Reasons include hangdowns and rope
getting caught on rocky areas which
produce major safety issues.
Response: See response to Comment
128 regarding hangdowns and safety
concerns. Current sightings data show
whales occurring in waters greater than
100 miles (185.2 km) offshore. Data also
suggest that right whales, humpback
whales, and fin whales all occur at the
edge of canyons. For example, northeast
sightings data places large whales at the
edge of the seafloor drop-off for George’s
Bank in the Gulf of Maine. See also
Comment 125. To ensure adequate
protection for large whales in these
areas, NMFS believes groundline
regulations put forth in this final rule
are appropriate.
Comment 135: Several commenters
emphasized their belief that low-cost
alternatives to sinking line were needed
before there are any requirements for
groundlines to be composed exclusively
of sinking line. They urged NMFS to
conduct more research on low-cost
alternatives. Several commenters
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requested that NMFS include a low cost
alternative in the FEIS based on
research by the NMFS Gear Team. The
commenters stated that, if this is not
included, NMFS should indicate in the
FEIS the agency’s commitment to
developing a low-cost alternative prior
to phasing in gear modifications. The
commenters cited page 3–41 of the
DEIS, Alternatives Considered but
Rejected, and stressed the importance of
a low-cost alternative to reducing
groundline profile for New Jersey
fishermen; commenters believe the data
are already available to support/
implement low profile line.
Response: NMFS has sought
comments and considered many
proposals from the ALWTRT and
public, and no suitable, low cost
alternative to sinking and/or neutrally
buoyant line has been identified. In the
absence of an alternative to sinking and/
or neutrally buoyant groundline that,
amongst other factors, is low cost to
industry, enforceable and also reduces
serious injury and mortality to large
whales, NMFS is implementing a
sinking and/or neutrally buoyant
groundline requirement in this final
rule. Research continues on alternative
approaches to those contained in this
final rule. NMFS plans on further
discussing the concept of low profile
line with the ALWTRT at the next
meeting.
Comment 136: Several commenters
requested that, if a sinking/neutrally
buoyant groundline is implemented,
NMFS should: (1) Allow 2,000-lb
(907.2-kg) weak links in offshore areas;
(2) exempt the top line of gillnets; (3)
exempt the bottom third of up and
down lines; (4) establish a 1.03 specific
gravity standard; (5) extend the phasein period so fishermen can amortize
rope replacement costs; (6) conduct
research to improve sinking line
durability; (7) explore whether rope
manufacturers can produce sinking line
that meets federal requirements; and (8)
consider the safety issues of working
with sinking line.
Response: NMFS does not recognize a
link between weak link breaking
strength and sinking or neutrally
buoyant groundline. Top lines of
gillnets are not required to be composed
of sinking or neutrally buoyant line.
Composition of up and down line or
buoy lines are currently regulated in 3
areas, Cape Cod Bay, SAM West, and
SAM East, during seasonal periods.
During these seasonal periods buoy line
composition does allow the bottom
third to be composed of floating line.
Buoy line composition, floating versus
sinking or neutrally buoyant, is not
regulated in all other ALWTRP areas.
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NMFS has included a definition of
neutrally buoyant or sinking line
specifying a specific gravity in this final
rule. The final rule does require sinking
and/or neutrally buoyant groundline 12
months after publication of the final
rule. NMFS, rope manufacturers, and
the fishing industry continue to work on
the durability issue. However, NMFS
believes the phase-in period
implemented in this final rule is still
warranted to reduce the serious injury
and mortality of large whales due to
entanglement in commercial fisheries in
order to meet NMFS’ mandates under
the MMPA and ESA. NMFS has
determined that manufacturers have
produced line that meets the standard
required by this final rule. Additionally,
NMFS has considered safety issues of
working with sinking line and will
continue to consider safety with the
ALWTRT.
Comment 137: Many commenters
requested that NMFS develop a rope
buy-back program. The commenters
support the program for the following
reasons: (1) It would ease the burden of
switching to sinking groundline (e.g.,
help absorb financial burdens and
defray the higher cost of sinking rope);
(2) it would encourage fishermen to
change over to sinking/neutrally
buoyant groundline earlier than the
proposed implementation date; and (3)
a line recycling/buyback program is the
only acceptable solution for taking care
of miles of useless poly line.
Response: NMFS agrees that buyback
programs are a viable option for the
reasons stated and several programs
have been executed in states along the
eastern seaboard. See responses to
Comments 117, 138, 139, and 140
regarding Massachusetts, Mid-Atlantic,
and Maine gear buyback program
activities.
Comment 138: One commenter
mentioned the gear buyback pilot
program, in which 300 Massachusetts
inshore lobster fishermen participated
and 300,000 lbs (136,078 kg) of floating
groundline were collected. The
commenter hopes this pilot program
will serve as a model for other states as
gear modification requirements take
effect.
Response: NMFS agrees and, in
collaboration with NFWF, administered
a similar buyback program in the MidAtlantic during January 2006. This
exchange program is also an effort to
remove floating groundlines between
traps/pots. State and/or federally
licensed/permitted commercial trap/pot
fishermen in New Jersey, Maryland,
Delaware, Virginia, and North Carolina
were eligible to participate. In addition,
the State of Maine is initiating a
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buyback program in 2007 (see responses
to Comments 117, 137, 139, and 140).
Comment 139: One commenter
believes that fishermen will not be able
to bear the full economic burden of the
proposed regulations. One commenter
states that a Congressional budget
earmark for multi-year poly buyback
and rope exchange was requested for
Maine to coincide with proposed low
profile implementation dates (2007–
2009).
Response: The social impact analysis
included in the FEIS examines the
economic burden posed by the
alternatives and the likely effect on the
economic viability of fishing operations.
The analysis identifies vessel segments
that may be heavily impacted by the
requirements and suggests that under
Alternative 6 Final (Preferred), a limited
number of small vessels are most at risk
when comparing annual compliance
costs to average per-vessel revenues.
Current and future groundline buyback
programs may help defray the
compliance costs for many vessels.
Comment 140: One commenter stated
that The Ocean Conservancy is working
closely with the State of Maine, Maine
Lobstermen’s Association (MLA), and
Southern Maine Lobstermen’s
Association to secure funding to assist
fishermen with line replacement.
Response: NMFS confirms that
several entities in Maine have been
working to establish a line replacement
program. The Gulf of Maine Lobster
Foundation has been identified to
develop and conduct a line replacement
program in 2006 and 2007. The Gulf of
Maine Lobster Foundation is currently
administering the program with 1.9
million dollars they received via a
Federal grant.
Comment 141: Many commenters
asked NMFS to consider other
regulations such as what the NEFMC is
considering for protecting deep sea coral
in canyons. One commenter stated that
sinking groundline will get caught on
deep sea coral and suggested that fishers
are asked to use floating groundline
only in canyons. Others commenters
stated that chafing of rope would cause
gear loss and the bottom would get torn
up by the rope.
Response: NMFS acknowledges the
impacts of sinking groundline, but
NMFS believes that in many areas the
industry can develop fishing practices
to address any difficulties in
transitioning from floating to sinking
and/or neutrally buoyant groundline.
NMFS will further discuss low-profile
groundline for other areas at the next
ALWTRT meeting. Also, see response to
Comment 128.
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Comment 142: One commenter would
like to see a clause that, for pots less
than 15 or 20 feet (4.6 or 6.1 m) apart,
that sinking line is not required.
Response: NMFS recognizes that this
configuration, 15–20 feet (4.6–6.1 m)
groundline, seeks to minimize the
amount of groundline, which is a
positive step toward the overall
reduction of line in the water. However,
NMFS is not able to exempt this
configuration. NMFS will be discussing
the concept of low profile groundline
further with the ALWTRT at the next
meeting, and will be providing the
ALWTRT with comments such as this to
consider.
Comment 143: One commenter stated
that, in the waters where he fishes, one
must use float rope because, while
setting the gear in 50 fathoms (91.4 m
or 300 ft), by the time it hits bottom, it
is at 70 or 80 fathoms (128.0 m or 420
ft to 146.3 m or 480 ft) because it will
be carried by the currents a half or 3⁄4
of a mile (0.8 or 1.2 km) before it hits
bottom.
Response: NMFS recognizes there are
many unique physical environments
that fishermen contend with while
fishing. The issue in this case appears
to be the delay in time from the last trap
being deployed from the vessel, the
trawl hitting bottom, and the drift of the
trawl during that time. Sinking and/or
neutrally buoyant groundline may
actually be an asset in this unique case
as the nature of this type of line (i.e.,
higher specific gravity compared to
floating line) may reduce the time from
the deployment of the last trap from the
vessel until the trawl hits the ocean
bottom.
Comment 144: One commenter
believes that in Grand Manan Channel,
where he fishes, it is impossible to
continue business using sinking rope.
His reasons for this include the rocky
habitat and the tide in the area.
Response: NMFS has worked with
industry in the Grand Manan Channel
in the process of developing sinking
and/or neutrally buoyant groundlines.
NMFS has had discussions with some
fishermen regarding the successful use
of sinking and/or neutrally buoyant
groundline in this area.
Comment 145: Two commenters
requested an exemption from sinking
groundline requirements in waters
deeper than 100 fathoms (182.9 m or
600 ft) along/in rocky canyons due to
their jagged topography. Use of sinking
groundline in these areas would cause
hangdowns and rope getting caught,
which is a big safety issue.
Response: NMFS is not able to exempt
these areas at this time. See response to
Comment 125 in reference to whale
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habitat and rocky bottoms. See response
to Comment 128 in reference to
hangdowns and safety issues.
Comment 146: One commenter
supports the 280-fathom (512.1-m or
1,680-ft) groundline exemption as long
as gear is marked and NMFS has a
formal mechanism to reconsider this
exemption if data show whales feeding
at these depths or become entangled in
gear fished at these depths.
Response: NMFS appreciates the
support of the 280-fathom (512.1-m or
1,680-ft) groundline exemption. There is
no provision for groundline marking in
the ALWTRP, including in waters in
excess of 280 fathoms (512.1 m or 1,680
ft). NMFS will continue to discuss gear
marking to monitor strategies with the
ALWTRT to see whether additional gear
marking strategies are needed and
should be implemented in the future.
Comment 147: One commenter would
like to see use of sinking line separated
by lobster management areas. The
commenter said that in LMA 2, 90percent of fishermen fish on rocks and
cannot use sink line due to hangdowns/
hangups, which is a major safety factor
for fishermen. A few commenters
believed that the lobster fishery should
be exempt from having to use sinking
and/or neutrally buoyant line in LMA 3
deeper than 90 fathoms (164.6 m or 540
ft). This area is very rocky. Commenters
stated ropes would be on rocks and
would chafe off and cause ghost gear.
Another commenter stated that the
Maine coast should not be regulated by
‘‘a one-size-fits-all’’ strategy, and that
the state is divided into zones because
they could not manage the areas very
well by one-size-fits-all, because every
zone, every town, and every fisherman
has to do things differently (i.e., eastern
Maine has extreme tides and York
County on the other end of the state
does not have much tide). Another
commenter said the area south of
Stonington and Boothbay have mud on
the bottom, and Downeast has rocky or
ledgy bottom, so the areas should be
treated differently.
Response: The ALWTRP management
areas were modeled after the Federal
LMAs with some additional unique
areas also identified. NMFS has
conducted gear research in diverse
habitat areas along the coast of Maine
over the years and believes that fishing
could be successfully accomplished in
these areas using sinking and neutrally
buoyant groundline. See Response to
Comment 128 with respect to unique
bottom types and physical
environments.
Comment 148: Several commenters
questioned the durability of neutrally
buoyant tail warps. The commenters
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believed that warps made with neutrally
buoyant line were not lasting as long as
those made with floating line, causing
more frequent gear replacement.
Commenters stated the following
problems with neutrally buoyant tail
warps: (1) Increased chafing and
burring; (2) twisting of the line around
the traps; and (3) increased gear loss.
Response: There are currently many
choices for fishermen in selecting nonfloating line. The line manufacturers are
working closely with fishermen to
develop lines suitable for a variety of
fishing practices. NMFS notes that the
fishing industry from Maine to Florida
utilized sinking and/or neutrally
buoyant line successfully in a variety of
applications before the advent of
floating line. Some percentage of
fishermen today do not use floating
groundline for a variety of reasons.
NMFS believes that the industry can
develop work practices that will address
the difficulties in transitioning from
floating groundline to sinking and/or
neutrally buoyant groundline. The
potential for hangdowns and ghost gear
may increase (see response to Comment
149).
Comment 149: One commenter said
that he went out with a few others and
tested the groundline/tail warp. The
commenter went out with an
underwater robotic camera and went
from Swans Island to Jericho Bay to Isle
au Haut to Deer Isle Thoroughfare. The
commenter said that they put the
camera down on a lot of traps and the
ten fathom (18.3 m or 60 ft) tail warp
was 2–3 feet (0.6–0.9 m) off the bottom.
The commenter believed that this works
even though some others were 15–18
fathoms (27.4 m or 90 ft-32.9 m or 108
ft) and standing 5–6 feet (1.5–1.8 m).
Response: NMFS appreciates this
report on demonstrated line
performance. NMFS will pass this
comment on to the ALWTRT for
consideration when low profile
groundline is further discussed.
Comment 150: One commenter said
that at a recent TRT meeting, a whale
expert stated that as long as there is one
piece of line in the entire Atlantic
Ocean that it poses a serious threat to
the right whale. The commenter
believed that the comment sums up
everything and that NMFS will
eventually try to take away line all
together, not just the ones discussed in
the plan. The commenter said that
fishing cannot be done without rope,
and the technology is not there to do so.
Response: NMFS recognizes a variety
of opinions exist on these issues. The
options considered in this rulemaking
did not include removal of all lines as
NMFS recognizes this is not a
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technically and operationally feasible
option.
Comment 151: For trap/pot gear, one
commenter recommended
implementing groundline modifications
from September 1 to March 31 rather
than to May 1. The commenter believes
this will reduce gear loss and difficulty
retrieving lost gear.
Response: The times and areas
identified for gear modifications are
based on whale sightings data. April
and May are months when whales are
expected to occur in the Mid-Atlantic.
NMFS believes the September 1 through
May 31 time period in the Mid-Atlantic
is appropriate. Thus, the gear
modifications that reduce the threat of
serious injury and mortality due to
entanglement in gear are required for
that gear type during these months.
Comment 152: One commenter states
that 17-fathom Rocks area and wrecks
should be exempted from groundline
requirements because their line gets
caught and can cause gear loss.
Response: NMFS recognizes that all
rocky bottoms and wrecks present a risk
of hangdowns for all gear types. NMFS
also recognizes that sinking and/or
neutrally buoyant line has been fished
successfully coastwide for many years
by a variety of gear types through the
development and implementation of
unique work practices. The 17-fathom
Rocks area mentioned by the commenter
has a compliance date 12 months after
publication of this final rule, similar to
other areas. Also see response to
Comment 128 regarding sinking and/or
neutrally buoyant groundline.
Comment 153: One commenter stated
that sinking/neutrally buoyant
groundline is the most significant
feature in the DEIS. The commenter also
stated that, since it is not fully required
until 2008, it is difficult, if not
impossible, to review the effectiveness
of this plan before 2012.
Response: NMFS appreciates the
comment on reviewing the effectiveness
of the plan and has created a Status
Report Review Committee as an
outcome of the 2005 ALWTRT Meeting
to discuss these issues. NMFS believes
that effectiveness will be discernable
before 2012.
Comment 154: Several commenters
stated that none of the alternatives
establish a mandated phase-in time for
sinking groundline. One commenter
stated that, instead of relying on
requiring a certain percentage of traps to
be re-rigged with sinking/neutrally
buoyant groundline by predetermined
dates before 2008, the alternatives rely
on incentives of unknown effectiveness
to encourage increased use of sinking/
neutrally buoyant groundline before
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57137
2008. Further, the commenter stated
that incentives allow vessels to enter
areas otherwise closed to fishing
because of large aggregations of right
whales. The commenter stated that the
DEIS does not contain any information
about how many fishermen operate in
those areas or how many might convert
their groundline before 2008 as a result
of being given access to those areas.
Response: Several of the alternatives
establish a mandatory date for the use
of sinking and/or neutrally buoyant
groundline. The commenter is correct in
stating that the alternatives do not work
on a percentage of traps but instead
require all gear be converted by an
established date. NMFS believes the
required gear modifications reduce the
risk of entanglement to the large
aggregations of whales referenced by the
commenter.
None of the alternatives in the FEIS
remove time-area closures. In fact,
newly regulated gillnet and trap/pot
fisheries are required to abide by the
current time-area closures for these gear
types. The commenter may be referring
to the number of vessels allowed to
enter DAM areas. DAM announcements
are unpredictable, making it difficult to
estimate the number of vessels affected.
Chapter 5 of the FEIS estimates the
number of additional vessels that could
be affected under the alternatives. The
removal of the DAM program and the
interim expansion of the SAM zone are
designed to address the unpredictability
of large whale distribution, and they
will be replaced with broad-based gear
modifications.
Comment 155: Several commenters
are already rigging their gear with
sinking groundline due to SAM, DAM,
Massachusetts requirements, and the
recent buyback program as well as
individual preferences.
Response: NMFS acknowledges this
fact and notes these actions may
mitigate the costs of the requirements of
this final rule.
Comment 156: A few commenters
were concerned that having to use
sinking/neutrally buoyant groundline
will jeopardize their ability to make a
living as fishermen in Maine.
Response: Chapter 7 of the FEIS
identifies vessel segments that may be
heavily impacted by comparing average
vessel revenues with compliance costs.
The analysis suggests that under
Alternative 6 Final (Preferred), a limited
number of small vessels are most at risk;
about half of these are Class I vessels
operating in Maine waters. While these
vessels may still realize high costs
relative to revenues, fishermen have
some options to try to mitigate the costs.
For example, the impacts of converting
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to sinking and/or neutrally buoyant
groundline may be defrayed, in part, by
current and future groundline buyback
programs operated by NMFS and other
partners. Further, NMFS has considered
concerns about sinking and/or neutrally
buoyant groundline in Maine in
developing its preferred alternative,
identifying additional areas off the coast
of Maine that would be exempt from
ALWTRP requirements. Expansion of
the exempted areas would reduce the
economic burden on Maine lobstermen
without increasing entanglement risks.
In addition, although the requirements
under Alternative 6 Final (Preferred)
may impose significant costs within the
first year after publication of the final
rule (to convert all groundline to sinking
and/or neutrally buoyant groundline),
fishermen may be able to distribute the
cost of the new gear over its useful life
by seeking a loan. After the first year,
ongoing costs would be significantly
lower as fishermen would only need to
replace worn-out and lost gear.
Comment 157: One commenter said
that a consequence of the four
alternatives (Alternatives 2, 3, 4, and 6)
would be that because sinking
groundlines are too dangerous to
employ, lobstermen will be forced to
fish single traps in areas where they
normally fish pairs, triples, or small
trawls. The commenter also said that
this will be an incredible economic
burden to fishermen and it will double
the amount of surface lines and buoys.
Response: See Response to Comment
128 regarding safety. The social impact
analysis included in the FEIS examines
the economic burden posed by the
alternatives and the likely effect on the
economic viability of fishing operations.
The analysis identifies vessel segments
that may be heavily impacted by the
requirements and suggests that under
Alternative 6 Final (Preferred) a limited
number of small vessels are most at risk
when comparing annual compliance
costs to average vessel revenues.
Contrary to the commenter’s assertion
that the alternatives would increase the
amount of surface line, the alternatives
are specifically designed to reduce the
amount of fishing line in the water
column by requiring sinking and/or
neutrally buoyant groundline and by
extending sinking buoy line
requirements at the surface to new
fisheries not currently covered by the
ALWTRP. In addition, NMFS is
currently performing related research on
vertical line by examining the
geographic distribution of vertical line
relative to whale distribution. This
research will help characterize how
ALWTRP requirements and other
regulatory changes have influenced risk
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from vertical line. Additionally, NMFS
has discussed and will continue to
discuss options to reduce risk associated
with vertical line with the ALWTRT.
Comments on Low Profile
NMFS solicited comments and
information from the public on issues
related to ‘‘low profile’’ groundline (e.g.,
prey distribution, large whale
distribution and behavior, and methods
for reducing the profile), and received
numerous comments. As many of those
comments are not directly related to the
present rulemaking action, this
preamble does not respond to all of the
‘‘low profile’’ comments received during
the public comment period in this rule.
NMFS will provide all comments
regarding low profile to the ALWTRT at
the next meeting when low profile
groundline will be discussed further.
NMFS and the ALWTRT will have an
opportunity to review and consider
these comments at that time.
Comment 158: One commenter said
that the state of Maine low profile
research that has been done with the
underwater camera has not been taken
into consideration by NMFS.
Response: As noted in the preamble to
the proposed rule and DEIS, NMFS was
unable to support using ‘‘low profile’’
groundline in the development of this
rulemaking action. NMFS identified
additional research and analysis
necessary to determine whether
lowering the profile of groundline to
depths other than the ocean bottom
reduces the potential for large whale
entanglement in certain areas.
Additionally, NMFS determined that
the depth to which the groundline
profile could be reduced needs to be
established after more information is
collected and analyzed on prey
distribution, large whale distribution
and behavior, and methods for reducing
the profile of groundline. NMFS would
need to define ‘‘low profile’’ line in
such a way that it is enforceable, is
operationally feasible for fishermen, and
reduces the risk of entanglement.
Presently, NMFS and others are
researching all of these issues. For
example, NMFS has supported
groundline studies by Maine DMR since
2003, including use of a Remote
Operating Vehicle (ROV) to investigate
groundline profile and the experimental
testing of low-profile groundline. During
the development of this final rule,
NMFS also conducted a series of
workshops in September 2005 to gather
information on low profile groundline,
which included discussion of Maine’s
research, and was discussed at the
December 2006 ALWTRT meeting. In
addition, NMFS solicited comments and
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information on ‘‘low profile’’ groundline
through the public comment process for
this rulemaking. Thus, states and fishing
industry are working with NMFS and
the ALWTRT to determine if emerging
technology exists to allow a
conservation equivalent gear
modification to sinking and/or neutrally
buoyant groundline in identified areas.
NMFS may consider ‘‘low profile’’
groundline in the future, and will be
further discussing these issues with the
ALWTRT at the next meeting.
Comment 159: One commenter stated
that sinking line between anchors or
concrete blocks and the traps is
problematic as the line wraps around
these anchors. The commenter believed
a 6-fathom (11.0-m or 36-ft) piece of
floating line or shorter piece (e.g., one
to three fathoms (1.8 or 6 ft to 5.5 m or
18 ft) is necessary in this area to avoid
gear loss and would not affect risk
reduction.
Response: Based on this comment
regarding the line between traps and
anchors, and review of the groundline
definition, NMFS finds that the
definition does not cover this portion of
the gear. (The groundline definition
‘‘with reference to trap/pot gear, means
a line connecting traps in a trap trawl,
and with reference to gillnet gear, means
a line connecting a gillnet or gillnet
bridle to an anchor or buoy line.’’)
NMFS did not specifically seek or
receive public comment on the
groundline definition related to the line
between traps and anchors, and
accordingly cannot make any
adjustments to the definition at this
time. NMFS will investigate this gear
configuration through contact with
fishermen and states to determine how
common a practice it is in trap/pot
fisheries, determine the type of line
used in this portion of the gear, quantify
potential risk if floating line is used,
determine any new issues that may be
raised by requiring sinking and/or
neutrally buoyant line in this area of the
gear, and discuss the appropriate
management response with the
ALWTRT at the next meeting.
Comment 160: One commenter said
that more research on using low profile
groundline (i.e., groundlines that float
between traps/pots at a height no greater
than 2 to 4 feet (0.6 to 1.2 m)) should
be pursued by NMFS as an
administrative procedure.
Reponse: Low profile groundline is
not being required in this final rule.
However, as noted earlier in this
preamble, NMFS will be further
discussing the concept of low profile
groundline with the ALWTRT at the
next meeting.
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Comments on Gear Marking
Comment 161: Several commenters
believe NMFS (and the Gear Research
Team) need to devise a better line
marking strategy to get more
information about entanglements and
enhance mitigation efforts. Specifically,
commenters urged NMFS to require
different colors to indicate the type and
location of fishing gear. Several
commenters suggested putting a red
tracer/colored tracer fibers in floating
groundline midway between each trap
to see where the whales get caught in
the gear. Colored tracer fibers could be
input/twisted in during the
manufacturing of the line; one
commenter further states that no cost
estimates exist for color-coding into new
line manufacturing. Many commenters
believe the marking should identify
fishery, area fished, and part of line,
such that sinking/neutrally buoyant
groundline is distinguishable from
floating groundline or buoy line.
Another commenter suggested NMFS
should develop stainless steel or nylon
type bands that can be crimped around
a line, or chips that can be inserted into
the line, coded with fishermen
identification or fishery/gear/area
information, for all fixed gear fisheries
and waters along the eastern seaboard.
The commenters suggested that the
marking should indicate state and gear
type and should apply coast-wide.
Several other commenters suggested
gear marking requirements that are more
consistent with current State, Federal
FMP, and other TRT requirements.
Response: NMFS considered current
State, Federal, and other TRT
requirements when finalizing the gear
marking requirements in this final rule.
Through this final rule, NMFS will
require specific color coding for
fisheries and areas not previously
required to mark gear. All specified gear
in specified areas must be marked with
a color code that represents gear type
and location. NMFS has tested stainless
steel or nylon type bands used around
the line, and found that this causes a
safety issue when the band gets caught
in the hauler. NMFS also found that
these bands wear out the line when
being hauled, which in turn destroys the
integrity of the line. NMFS is currently
working on a chip technology that can
be inserted into the line and coded with
fishermen identification for the entire
eastern seaboard which will help to
more easily identify gear in the water.
NMFS will discuss this technology with
the ALWTRT in the future.
Comment 162: One commenter
suggested that NMFS require that
inshore gear at least be marked
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sufficiently to tell if it is risky for
whales.
Response: NMFS agrees and confirms
that provision was proposed and is now
being implemented in this final rule.
Gear in ALWTRP inshore management
areas will be required to have one 4inch (10.2-cm) colored mark midway
along the buoy line in the water column
as well as surface buoy markings. Many
of these inshore areas are also statemandated to mark traps and buoy
systems. NMFS is currently working on
developing chip technology that can be
inserted into the line and coded with
fishermen information for the entire
eastern seaboard which will help to
more easily identify gear in the water.
NMFS will be discussing this
technology with the ALWTRT in the
future.
Comment 163: One commenter
supports the use of red tape to mark gear
in LMA 2, but wants to make sure that
it is clarified that if less than 60 fathoms
(109.7 m or 360 ft), the mark is in the
center of the buoy line.
Response: Under this final rule NMFS
will not be adopting the proposed gear
marking scheme for buoy lines as
referred by the commenter. Rather, the
gear marking scheme will require one 4inch (10.2-cm) colored mark midway
along the buoy line in the water column,
regardless of the length of the line.
NMFS believes this requirement is in
line with what the commenter was
suggesting.
Comment 164: Two commenters
urged NMFS to require marking of all
surface buoy systems in federal and
state waters in a manner that identifies
the owner/vessel such as vessel name
and/or license/permit number and/or
fishery.
Response: NMFS will require trap/pot
and gillnet gear to mark all surface
buoys to identify the vessel or fishery
with one of the following: The owner’s
motorboat registration number, the
owner’s U.S. vessel documentation
number, the federal commercial fishing
permit number, or whatever positive
identification marking is required by the
vessel’s home-port state.
With regard to gear markings that
yield individual vessel information,
many of the state and Federal FMPs
currently require marking of buoys and/
or traps with individual vessel
identification. NMFS plans to continue
to work with state fisheries agencies to
investigate gear marking coast-wide and
identify gaps in marking of surface gear,
gillnets, and traps.
Comment 165: One commenter
believes buoy lines that are 50 fathoms
(512.1 m or 1,680 ft) or less should have
one 4-inch (0.1 m) colored mark unique
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to a fishery and state and for buoy lines
above 50 fathoms (512.1 m or 1,680 ft)
should have two marks.
Response: Based on implementation
considerations and technology presently
available, NMFS believes the final gear
marking scheme is appropriate. If more
promising techniques become available
in the future, NMFS will discuss these
further with the ALWTRT. See response
to Comment 163.
Comment 166: One commenter
suggested marking buoy lines greater
than 20 fathoms (36.6 m or 120 ft) once
midway in the lines and for buoy lines
greater than 100 fathoms (182.9 m or
600 ft) marking once at least every 50
fathoms (91.4 m or 300 ft) for sinking
and floating buoy lines.
Response: See response to Comment
163.
Comment 167: Several commenters
supported marking buoy lines with 1
four inch (0.1 m) mark every 10 fathoms
(18.3 m or 60 ft). One commenter
supported the proposed gear marking
scheme as long as it is not too
complicated and fishermen have enough
time to comply. Another commenter
stated that he would mark buoy lines
twice if it would help determine the
origin of gear. One commenter stated
that, at the last ALWTRT meeting, the
team agreed that any additional
requirements would be decided by a
gear group.
Response: See response to Comment
163. NMFS did solicit gear marking
options from the ALWTRT previously,
and will continue to discuss any other
appropriate gear marking schemes/
strategies with the ALWTRT.
Comment 168: Many commenters
object to the proposed scheme of
marking buoy lines with a 4-inch (0.1
m) mark every 10 fathoms (18.3 m or 60
ft). Commenters objected to the
proposed marking scheme for the
following reasons: (1) It would be
impossible in deep water; (2) the tape
will not stick to wet rope, nor will paint.
While these markings could be applied
to rope when dry, adjusting the marks
at sea is impossible; (3) marking
techniques lose their visibility within a
few weeks in the water as algal growth
accumulates on the ropes making the
mark hard to discern and basic wear and
tear of marks; (4) gear marking would be
difficult to implement as line is spliced
or fouled over the course of its useful
life; (5) there would be a problem in
trying to figure out whether the space
between marks is exactly ten fathoms
(18.3 m or 60 ft) when the lines are
spliced due to broken buoys, lines etc.;
(6) it will be tough to mark at sea,
especially given temperature, sea state,
and safety considerations; (7) the
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proposed scheme would only identify a
buoy line, but not a fishery or even a
region where the gear was fished (i.e.,
no unique identifier), so this limits the
amount of information that can be
tracked and evaluated; (8) it is too time
consuming, costly, impractical, and
unworkable; (9) the marking scheme is
generic and limited marks will not
provide much information; (10) too
many areas will not have marking
requirements (e.g., exempted areas,
recreational gear, Canadian waters); (11)
gear loss would be too much with using
the new gear marking; (12) it will be a
financial burden to fishermen, without
much chance for results that are useful;
(13) buoys and traps are already marked
under current lobster fishing rules; and
(14) it would be hard to enforce given
the large number of recreational
lobstermen. One commenter states that
if this provision is adopted, it might
tempt fishermen to use a different color
code or no marking at all to divert
attention away from their sector.
Response: Based upon these
comments, NMFS changes the
regulations through this final rule, to
require all fisheries to mark buoy lines
with one 4-inch (10.2 cm) colored mark
midway along the buoy line in the water
column and mark surface buoys.
Requiring only one mark alleviates all
concerns regarding safety and other
practicality issues raised by
commenters. NMFS will continue to
discuss gear marking strategies,
factoring in safety and other concerns,
with the ALWTRT.
Comment 169: Some commenters
stated that fishers will be reluctant to
comply with the marking scheme
because there is no direct risk reduction
to whales.
Response: NMFS believes that,
although there is no direct risk
reduction to whales, the information
obtained from gear marking may assist
in the management of incidental whale
entanglements.
Comment 170: One commenter
suggests more frequent marking of buoy
lines (e.g., every 5 fathoms (9.1 m or 30
ft)).
Response: See response to Comment
163.
Comment 171: Two commenters
suggest marking the buoy lines less
frequently. One commenter believes that
requiring marking in lesser increments
may increase compliance. One
commenter believes one mark in the
middle of a rope is sufficient as there is
no difference between having one mark
or ten marks.
Response: See response to Comment
163.
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Comment 172: One commenter
believes that in the various gear marking
systems proposed throughout the
history of the ALWTRP, NMFS has
routinely failed to: (1) Incorporate and
capitalize on gear marking already
required in the fishery under existing
take reduction regulations or FMPs; (2)
augment the existing gear marking
system with more frequent marking
requirements to increase the probability
of identifying gear type and parts (e.g.,
buoy line from groundline); and (3)
devise a marking system that is easy,
safe, and technologically feasible to
implement.
Response: NMFS has capitalized on
and considered other management plans
as well as take reduction regulations
regarding gear marking requirements.
NMFS did consider more frequent
marking in the proposed gear marking
scheme; however, based on public
comments that this is not operationally
feasible, NMFS came up with the gear
marking scheme that is implemented in
this final rule. NMFS is currently
researching a future marking system that
is easy, safe, and technologically
feasible to implement.
Comment 173: One commenter states
than an area-specific scheme may
complicate the marking strategy.
Response: NMFS does not believe that
an area-specific scheme would
complicate the marking strategy because
an area-specific scheme already exists.
However, to alleviate any possible
complications, NMFS is grouping
requirements for all trap/pot fisheries
and for all gillnet fisheries. Where
possible NMFS is expanding gear
marking schemes to be consistent with
existing color schemes.
Comment 174: One commenter stated
that fishermen would have to replace
the buoy line markings every time they
move gear from shallow (e.g., 3 fathom
(5.5 m or 18 ft)) to deeper water (e.g., 30
fathom (54.9 m or 180 ft)) such as what
occurs along the hard bottom ridges and
reefs in and beyond Casco Bay. The
commenter stated that it would be time
prohibitive to have to keep replacing the
lines.
Response: NMFS believes that line
would not have to be replaced, but
marks would have to be changed when
gear is moved from shallow to deeper
water in all areas and when buoy lines
are lengthened.
Comment 175: One commenter
supports microchip tracer technology
for marking gear.
Response: NMFS agrees and is
currently working on developing a
microchip technology for marking gear.
Comment 176: Several commenters
agree with experts who request that
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ropes be identifiable in aerial images of
entangled whales.
Response: It is difficult to identify the
gear on entangled whales in aerial
images at present, but NMFS is
exploring technologies such as
microchip technology that will help to
identify gear that is entangling whales.
Comment 177: One commenter stated
that gear marking may be a problem to
enforce because not many people know
how much 10 fathoms (18.3 m or 60 ft)
is.
Response: As a result of the difficulty
in implementation, NMFS is changing
the proposed buoy line marking
requirement to one 4-inch (10.2 cm)
colored mark midway along the buoy
line in the water column.
Comment 178: One commenter would
like the marking of surface buoys to be
consistent with the bottlenose take
reduction plan.
Response: The Bottlenose Dolphin
Take Reduction Plan (BDTRP) final rule
published on April 26, 2006 (71 CFR
24776), does not require the marking of
surface buoys.
Comment 179: One commenter stated
that the proposed scheme does not
include any marking of groundline.
Commenters suggested that NMFS
require all parts of the gear to be
marked, including sinking groundline to
monitor its effectiveness; a specific
color should be used to identify sinking/
neutrally buoyant groundline from
floating groundlines or buoy lines.
NMFS should work with rope
manufacturers to designate such color
codes.
Response: This final rule does not
require the marking of groundline.
NMFS did not propose marking
groundlines through this rulemaking
due to the time and cost burden
associated with requiring sinking and/or
neutrally buoyant groundline coupled
with the lack of a suitable gear marking
technique that reduces burden to
fishermen (e.g., costs and labor) given
the amount of line used in these
fisheries. NMFS will continue to discuss
gear marking strategies with the
ALWTRT and support research and
development of promising marking
technologies.
Comment 180: One commenter
wanted to know what studies have been
done in the Quoddy Head area.
Specifically, examining the current. The
current is heavy and will wash marks
off. The commenter also questioned the
gear marking of every 10 fathoms (18.3
m or 60 ft) and believed that it would
be a lot of marking due to the amount
of buoy line needed.
Response: NMFS is aware and has
considered the impact of the heavy
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currents in the Quoddy Head area (see
the report ‘‘Load Measurements in
Lobster Gear’’ in NMFS’ Large Whale
Gear Research Summary (NMFS, 2002)).
There are many reliable techniques
available in marking or affixing the
color code: The line may be dyed,
painted, or marked with thin colored
whipping line, thin colored plastic, or
heat-shrink tubing, or other material; or
a thin line may be woven into or
through the line. In this final rule, the
gear marking scheme will require one 4inch (10.2-cm) colored mark midway
along the buoy line in the water column.
Comment 181: One commenter stated
that all gear-buoys and floats are marked
by law so there are 3,000 chances to
identify gear. The commenter said that
most of lines are marked 4 times with
license number, name, and sometimes
home port.
Response: NMFS understands that
there are requirements that both traps
and buoys be marked in many areas. To
improve the chances of identifying a
gear type when neither a trap or buoy
are recovered some identification on the
buoy line could be helpful. Under this
final rule, the gear marking scheme will
require one 4-inch (10.2 cm) colored
mark midway along the buoy line in the
water column. Additionally, trap/pot
and gillnet gear regulated by the
ALWTRP must mark all surface buoys to
identify the vessel or fishery with one
of the following: the owner’s motorboat
registration number, the owner’s U.S.
vessel documentation number, the
federal commercial fishing permit
number, or whatever positive
identification marking is required by the
vessel’s home-port state.
Comments on Weak Links
Comment 182: Several commenters
support the proposed use of weak links/
weak link regulations for the following
reasons: (1) Fishermen have been
cooperative in using them; (2)
considerable research has already been
done; and (3) weak links may reduce
drowning deaths, reduce rope wounds
at early entanglement stages, and lessen
the effects of entanglement by allowing
the whale to shed smaller lengths of
gear.
Response: The continued cooperation
and support from the fishing industry is
essential for the ALWTRP to achieve its
goals. NMFS is committed to gear
research and development and intends
to continue to support studies on weak
links, which add a level of protection
for large whales.
Comment 183: Several commenters
support weak link research. One
commenter suggested that NMFS
determine species-appropriate breaking
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strengths and the best number and
placement of weak links according to
gear type and use. Another commenter
stated that weak links on the buoy lines
should be designed to break. One
commenter believes that without further
research, NMFS cannot assume that the
benefits of weak links to survival of
whales are greater than the dangers
posed by weak links; this commenter
states that the greatest danger is using
untested methods that could result in
death and injury to whales that should
have been protected by other means.
Response: NMFS is committed to gear
research and development, and intends
to continue to support studies on weak
links to reduce interactions between
large whales and commercial fishing
gear. NMFS has gear laboratories and
research teams that specifically focus on
gear development and testing.
Additionally, NMFS contracts with
researchers, individuals, and companies
to develop gear solutions. Much of the
current take reduction plan measures
are based on the outcome of such gear
research (e.g., weak links) conducted
and/or funded by NMFS. NMFS
believes that weak links add a level of
protection for large whales, and in
combination with other mitigation
measures, serve as a valuable
conservation tool.
Comment 184: Numerous commenters
stated that weak links have never been
proven to reduce risk and that NMFS
relies too much on them. Several
commenters stated that lethal and lifethreatening entanglements are known to
have involved gear with weak links still
attached, which had breaking strengths
equal to or less than what NMFS has
proposed. One commenter stated that
weak link requirements in current
ALWTRP regulations have been in place
for nearly 5 years, yet the rate of large
whale entanglement has not been
reduced. The commenter believes that
the effectiveness of deploying weak
links on gear needs to be better analyzed
for entanglement prevention. Another
commenter suggested weak link failure
may be a result of where the weak links
are being placed in the gear.
Response: There is no evidence to
suggest that weak links, when designed
and used properly, are ineffective. Weak
links reduce the breaking strength of
traditional gear. The breaking strength
of weak links is based on the tractive
force of animals in addition to
commercial fishing practices (DeAlteris
et al., 2002). Weak links add a level of
protection for large whales and NMFS
intends to continue to support studies
on weak links to reduce entanglement
risk. See also response to Comment 183.
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Comment 185: One commenter agrees
with using weak links in gillnets more
than in buoy lines, but does not believe
that NMFS has proven that 1,100-lb
(499-kg) weak links are sufficiently risk
averse.
Response: NMFS believes that 1,100lb (499-kg) weak links reduce
entanglement risks by reducing breaking
strength of traditional gear, which
ranges from 3000 to 5000 lbs (1361 to
2268 kgs). The breaking strength of
weak links is based on the tractive force
of animals in addition to commercial
fishing practices (DeAlteris et al., 2002).
Should new information become
available that may warrant a change to
the weak link tolerances in gillnets,
NMFS will consider this new
information in consultation with the
ALWTRT.
Comment 186: Several commenters
disagreed with requiring five or more
weak links with a 1,100-lb (499-kg)
breaking strength per net panel. One
commenter stated that modifying gear
under the proposed weak link
regulations is not possible, as they will
incur great financial losses during
haulback. One commenter specifically
suggested conducting further research to
determine if this is operationally
feasible for the offshore gillnet fishery in
Maine.
Response: In developing the
appropriate gear modifications in this
area, testing has been done with
offshore vessels in the Gulf of Maine.
Testing showed no additional
operational problems beyond those
experienced in the course of traditional
fishing practices. NMFS worked closely
with commercial fishermen and the
state of Maine to develop weak links for
fishermen in this area.
Comment 187: A few commenters
questioned why NMFS is proposing to
retain the same breaking strength for
inshore fisheries while allowing greater
breaking strengths in offshore fisheries.
Several commenters stated that weak
link breaking strengths should be greater
for offshore fisheries. One commenter
believes that, for the lobster trap/pot
fishery, the weak links should be 1,500
lb (680.4 kg) offshore and 600 lb (272.2
kg) inshore, and should be in place from
Sept 1–Mar 31 only. Another
commenter would like to see a 1,000-lb
(499-kg) weak link or 1,500-lb (680.4-kg)
weak link versus a 600-lb (272.2-kg)
weak link in offshore waters so that
there is not as much gear loss during
bad weather.
Response: Several months of at-sea
testing of trap/pot gear has been
conducted and NMFS believes the
breaking strengths in this final rule for
inshore and offshore fisheries are
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appropriate. NMFS is reducing the
breaking strength for weak links in the
ALWTRP offshore management areas
from 2,000 lb (907.2 kg) to 1,500 lb
(680.4 kg) akin to the current weak link
requirement for SAM. There is not a
600-lb (272.2-kg) weak link requirement
in the ALWTRP offshore management
areas. If the commenter meant to say
ALWTRP nearshore management areas
as mentioned above, NMFS believes the
weak link requirements in this final rule
are appropriate. In developing the
appropriate breaking strengths, NMFS
considered tide, sea conditions, weather
conditions, load cell data, and size and
weight of gear.
Comment 188: One commenter would
like to see weak links for inshore pot
fisheries be 1,000 lb (499 kg) in case the
trap itself is considered a weight under
the regulations.
Response: NMFS does not consider
the trap itself to be a weight in the
regulations. In this final rule, the
ALWTRP inshore trap/pot management
areas will be required to have 600-lb
(272.2-kg) weak links. See response to
Comment 187.
Comment 189: One commenter stated
that the load testing information
presented at the 2003 and 2004 TRT
meetings does not support breaking
strengths as strong as presented for
many trap/pot fisheries, as well as
offshore fisheries. The proposed rule (70
FR 35903, June 21, 2005) notes that load
cell testing showed a strain of 320 lbs
(145.1 kg) was necessary to haul the
gear, therefore, allowing a breaking
strength of almost 4 times that is
excessive and likely to pose greater risk
to whales than is necessary.
Response: The Cordage Institute
establishes safety standards for rope,
and has come up with a safety factor, or
safe working load of 10 in applications
such as commercial fishing. See
response to Comment 187.
Comment 190: One commenter stated
that in Cape May, New Jersey, the
fishermen have a lot of trouble with 50foot (15.2-m) sport boats hanging on
buoys, and at night in canyons you can
see 20–30 boats hanging on every one of
the buoys. The commenter believed that
the 1,500-lb (680.4-kg) weak links could
not hold a 50-ton sport boat. The
commenter believed that this is the
biggest concern with the weak links in
the offshore fishery.
Response: NMFS will share this
information with law enforcement
officials and encourages the commenter
to work with local law enforcement in
an effort to address this issue.
Comment 191: One commenter
believes that it is inequitable to allow
gillnetters to use 1,100-lb (499-kg) weak
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link when traps/pots have to use 600-lb
(272.2-kg) buoy line weak links. One
commenter questions if a 1,100-lb (499kg) weak link is sufficient throughout
the coastline. The commenter stated that
while it is appropriate in some areas,
others areas like Stellwagen Bank and
Jeffreys Ledge may be able to use 600lb (272.2-kg) weak links. The
commenter is concerned about young
whales not being able to break free. The
commenter recommends that NMFS
explore feasibility of 600-lb (272.2-kg)
weak link for certain high-use areas
such as Stellwagen Bank, Jeffreys Ledge,
and other inshore areas. The commenter
states there have been no failures in
approximately 3,600 hauls.
Response: NMFS developed weak link
breaking strengths for gillnet and trap/
pot fisheries based on load cell testing
of surface systems as well as operational
issues. In this final rule, NMFS lowered
weak link breaking strengths for some
fisheries and management areas. NMFS
believes the weak link breaking strength
requirements in this final rule,
including those for Stellwagen Bank and
Jeffreys Ledge, are as low as is practical.
Further reductions, if required as broad
based management measures, could
jeopardize safety.
Comment 192: One commenter stated
that all state waters should be exempt
from weak link requirements for inshore
gillnets (strikenets).
Response: This final rule does provide
an exemption from the ALWTRP
requirements in bays, harbors, and
inlets in state waters where whales
occur rarely if at all. However, those
waters that are not exempt are subject to
the ALWTRP requirements. NMFS
believes anchored gillnet fisheries in
regulated state waters should be subject
to weak link requirements because large
whales are likely to occur in these areas
during the seasons specified under this
final rule.
Comment 193: One commenter
believes the breaking strength
calculation is not appropriate (i.e.,
considered by some to be ‘‘arbitrary’’)
and is only based on fishing practices.
Response: NMFS disagrees with the
commenter and believes that the weak
link requirements described in this final
rule are appropriate and based on
appropriate calculations. In developing
the appropriate breaking strengths,
NMFS considered tractive force of right
whales, tide, sea conditions, weather
conditions, load cell data, and size and
weight of gear (DeAlteris et al., 2002).
See response to Comment 183.
Comment 194: Several commenters
prefer 2,000-lb (907.2-kg) buoy line
weak links (rather than 1,500-lb (680.4kg)) from September 1–March 31
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because of issues related to weather,
wind, and tides throughout the fall and
winter. Further, the commenters state
that grappling is hazardous and stronger
links will reduce ghost gear. One
commenter believes there is no evidence
to require gillnets set in deep water to
have weak links. The commenter
questions whether they would be
recovered intact, especially given tidal
and storm impacts to nets.
Response: Gear research conducted by
NMFS and the fishing industry does not
support these concerns. NMFS believes
the weak link requirements described in
this final rule are appropriate. NMFS
collected load cell data in offshore areas
during the time period suggested by the
commenter, which support the
effectiveness of 1,500-lb (680.4-kg) weak
links. With regard to the hazards of
grappling, see response to Comment
128.
Comment 195: Several commenters
suggested method alternatives to the
proposed weak link configuration/
measures such as: (1) Rigging nets with
weak lines (ropes of appropriate
breaking strength) that meet breakaway
standards instead of with multiple weak
links. For example, if the breaking
strength of vertical breastlines are less
than 1,100 lb (499 kg), the commenter
believes a weak link should not be
required; (2) using 4 weak links per net
panel rather than 5, with a single weak
link in the center of the panel’s
headrope, and one at each end of the
headrope within the bridles; (3) using
one weak link between net panels plus
a weak link in the center of each net
panel and one at either end of net before
the anchor and buoy system; for the up
and down line, the commenter suggests
rope of appropriate breaking strength of
1,100 lb (499 kg); (4) using one weak
link in the middle of the panel and one
weak link in the bridle between nets
(instead of using of three weak links in
the float line of 50-fathom (91.4-m or
300-ft) net panels); and (5) using 1,100lb (499-kg) weak rope for the floatline.
Response: Based on public comments,
NMFS makes a change from the
proposed rule to allow two weak link
configurations for net panels in a string
[See Changes from Proposed Rule].
Details for the two configurations can be
found in the Anchored Gillnet section of
the Northeast Gillnet Waters section of
this preamble. For further description
and a diagram of the two configurations
see Figure 4 in this preamble. The
breaking strength of each weak link
must not exceed 1,100 lb (499 kg) and
the weak link requirements apply to all
variations in panel size. Elements of the
two weak link configurations are similar
to aspects of the above comments. In
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addition, if rope of appropriate breaking
strength is used throughout the floatline
or up and down line, or if no up and
down line is present, then individual
weak links are not required.
Comment 196: One commenter
supports one weak link at intervals no
less than every 25 fathoms (45.7 m or
150 ft) in gillnets.
Response: Based on gear research
conducted by the Gear Research Team,
NMFS believes weak links placed no
greater than every 25 fathoms (45.7 m or
150 ft) along the floatline for gillnet net
panels is an appropriate mitigation
measure for gear returned to port in the
Mid- and South Atlantic. The net panels
are typically 50 fathoms (91.4 m or 300
ft), so this requirement ensures one
weak link per net panel.
Comment 197: One commenter
opposes one 1,100-lb (499.0-kg) weak
link per panel for gillnets returning to
port. The commenter uses ‘‘strike nets’’
and catches croaker close to the beach
in New Jersey state waters from August
to November. The commenter states
there has been extensive observer
coverage in the last 4 years (72 observed
trips) and no reported entanglements.
Response: In the Mid-Atlantic, only
one weak link per net panel is required
for nets returning to port with the
vessel. To account for differences
between nets returning to port and those
not returning to port with the vessel,
more weak links per net panel will be
required for nets not returning to port.
NMFS acknowledges that few
interactions between large whales and
commercial fisheries have been
observed and recorded by NMFS
observers. These are rare events;
however, they are occurring at a rate
unsustainable for these large whale
populations.
Comment 198: One commenter
believed the 25-fathom (45.7-m or 150ft) weak link belongs between the net
and not on ends. The commenter claims
it is easier and less burdensome and it
also accomplishes the same thing.
Response: Based on research
conducted by the Gear Research Team,
NMFS believes that the configuration
specified in this final rule for net panel
weak links is the most appropriate
measure. See responses to Comments
195 and 196.
Comment 199: One commenter would
like clarification on the wording of weak
link for up and down lines as most
fishermen call them breastlines. One
commenter stated that weak links
should not be required in breastlines in
those fisheries where the breastline is
composed of twine.
Response: The up and down line is
defined as the line that connects the
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floatline and leadline at the end of each
net panel. For further details on weak
link configurations for net panels, see
response to Comment 195. NMFS notes
in this final rule that, if rope of
appropriate breaking strength is used
throughout the floatline or up and down
line (i.e., breastline) or if no up and
down line is present, then individual
weak links are not required. Thus, if the
breastline is composed of twine, as long
as it is of appropriate breaking strength,
then individual weak links would not
be required.
Comment 200: A few commenters
believe that the use of breakaways or
weak links in beach seine gear is going
to be a problem. They believe that if the
weak links break, the net will hang
down on the beach and the net will rip.
Also, the weak links will break when
hauling, and the 1,100-lb (499.0-kg)
weak link affects the hang.
Response: At this time, NMFS is not
regulating gillnets that are anchored to
the beach and subsequently hauled onto
the beach to retrieve the catch. This
fishing technique is known to occur on
the beaches of North Carolina. NMFS
will be discussing what the appropriate
management measures for this unique
fishery should be with the ALWTRT at
future meetings. In the meantime,
NMFS will be conducting outreach and
research on this fishery to support
future discussions with the ALWTRT.
NMFS will be coordinating with the
North Carolina Department of Marine
Fisheries to revise the definition for
beach-based gear to help ensure
landings are reported accurately for
beach-based gear versus gillnets, among
other issues.
Comment 201: One commenter said
that 1,500-lb (680.4-kg) weak links
cannot be purchased. The commenter
said that the person who makes weak
links will not make them because
nobody buys 1,500-lb (680.4-kg) weak
links.
Response: NMFS disagrees. Weak
links with a breaking strength of 1,500
lb (680.4 kg) are currently available on
the market.
Comment 202: One commenter states
that it seems clear from observations of
whales that they thrash upon becoming
entangled and this may reduce efficacy
of weak links. Perhaps placing a weak
link at the bottom of vertical lines
would allow an animal to pull free with
more ease but it can still wrap itself.
Response: Currently, little is known
about whales’ behavior upon
encountering gear. Weak links placed at
the bottom of the vertical line could
present safety issues as well as problems
retrieving gear. NMFS intends to
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continue to support studies on weak
links to reduce the risk to whales.
Comment 203: One commenter
suggests certain strengths of weak links
for different parts of the year.
Response: This final rule requires
weak link breaking strengths based on
management areas and does not have a
seasonal component to them. However,
in special management areas, weak link
breaking strengths are lowered during
certain times of the year when right
whales are present. The commenter is
encouraged to work with the NMFS
Gear Research Team to develop
additional gear research deemed
necessary.
Comment 204: One commenter said
that where he anchors in southern New
England, it is mostly mussels and hard
bottom. Usually, the net gets wrapped in
mussels and rocks and it will not go
anywhere when something hits it. But,
years ago, scallopers would hit his nets
and go right through them, taking that
section of the net right out, without
breakaways (i.e., weak links). The net
does not move when it is hit, it gets
shredded.
Response: NMFS recognizes that nets
not properly anchored can easily move
across the bottom, as well as up and into
the water column. Consequently,
research has been conducted to
establish anchoring requirements that
are appropriate for the weak links in the
gillnet panels.
Comment 205: One commenter was
concerned about weak links in net
panels south of 29°00′ N. causing gear
loss in the southeast because the gear is
hauled over the stern. The commenter
said that fishermen do not need weak
links in the southeast as gear is tended,
the nets are shorter, effort is low, and
the size of the fishery is small. The
commenter also said that fishermen are
required to move gear if a whale comes
near the gear.
Response: NMFS conducted research
on several vessels in the southeast
region and found that the non-shark
gillnet gear could be fished with weak
links. These weak link requirements are
similar to the Mid-Atlantic where some
fisheries are conducted similar to those
in the southeast. Weak links are one of
the broad-based gear modifications that
NMFS is implementing through this
final rule. However, in the Southeast,
weak link requirements are only
applicable to non-shark gillnet fisheries
(i.e., not shark gillnet fisheries).
Comment 206: Two commenters cited
problems with weak links and heavy
boating traffic. One commenter believed
that weak links are easily broken due to
heavy pleasure boat traffic. The other
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commenter stated a loss of 10-percent of
his buoys due to boat traffic.
Response: Pleasure boats causing loss
of surface systems is not necessarily due
to the weak link. Based on the result of
at-sea testing, NMFS believes the
breaking strength requirements are
appropriate.
Comment 207: One commenter states
that weak links are unnecessary in shoal
waters because they pose a problem
when changing lines, plus whales
would hit the bottom if they entered
these areas. However, the commenter
understands that whales could be in 40–
50 fathom (73.2 m or 240 ft–91.4 m or
300 ft) water.
Response: NMFS has determined
based on its understanding of current
fishing practices that placing weak links
as close to the buoy as operationally
feasible presents little problem when
changing buoy line, whether the trap is
in shoal or deep water.
Comments on Vertical Lines (or Buoy
Lines)
NMFS solicited comments and
information from the public on issues
related to vertical line (e.g., how whales
utilize the water column, gear
modification options). Those comments
related to this rulemaking action are
responded to below. Those comments
that are outside the scope of the present
rulemaking action are not responded to
in this final rule, but will be provided
to the ALWTRT at the next meeting,
when options for reducing risk
associated with vertical lines will be
discussed further. NMFS and the
ALWTRT will have an opportunity to
review and consider these comments at
that time. It is important to note that
NMFS provided the ALWTRT with a list
of management options to reduce risk
associated with vertical line to support
future discussion on this issue.
Additionally, NMFS is funding an
analysis to evaluate the effectiveness of
current and/or future fishing effort
reductions in decreasing the amount of
vertical line in the water column. This
information will be provided to the
ALWTRT at the next meeting to assist
in the discussion and development of
recommendations to NMFS on reducing
risk associated with vertical line.
Comment 208: A few comments were
received that claimed that the DEIS was
inadequate because it only dealt with
half of the entanglement risk to large
whales. The commenters referenced the
Johnson et al. (2005) analysis, which
was provided in the DEIS, and indicated
that entanglements occur in both
groundline and vertical lines on an
equal basis. Some commenters believe
NMFS has not quantified the net change
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in risk (between one buoy line or two)
or the biological impacts and has not
offered a compensatory risk reduction
measure.
Response: NMFS considered the
Johnson et al. (2005) analysis that
examined the fishing gear involved in
right and humpback whale
entanglements. According to Johnson et
al. (2005), any line rising into the water
column presents an entanglement risk to
large whales. While it may appear from
this analysis that buoy and surface
system lines represent a greater
entanglement risk to large whales than
groundlines do, both the authors of the
analysis and the DEIS note that it is
difficult to compare the relative risks
associated with these parts of fixed gear
for a number of reasons. There are many
uncertainties associated with
entanglements; for example, the history
of a particular entanglement may not be
fully reflected from the gear recovered
or the location of gear on a whale’s body
when an entanglement is first reported.
There are also biases associated with
entanglement reporting effort, as well as
a lack of information about the types
and amounts of gear currently in use. In
addition, it is possible that
entanglements in buoy lines are
reported more frequently at sea than
entanglements in groundline, as buoy
lines are easier to identify based on the
presence of a buoy or high flyer.
Groundline does not have any
distinguishing characteristics that
would make it easy to identify; thus,
this part of the gear can usually only be
identified if gear has been recovered
from an entangled whale, and even then
it is difficult to determine the part of the
gear that piece of line came from.
Johnson et al. (2005) state that, despite
gear recovery and/or identification, 44
percent of the entanglement events
analyzed in the study involved an
unknown part of the gear. The study
confirms that vertical lines and floating
groundlines pose risks for large whales.
NMFS believes that addressing the risk
associated with floating groundline by
requiring the use of sinking and/or
neutrally buoyant groundline will
reduce serious injury and mortality of
large whales due to incidental
entanglement in commercial fishing
gear. As noted in the DEIS and FEIS,
NMFS believes that further research and
discussions with the ALWTRT are
needed to address risks associated with
vertical line.
At this time, neither the ALWTRT or
NMFS is able to identify a viable option
for further reducing the risk associated
with vertical lines. NMFS has, in fact,
concluded that requiring the use of one
buoy line may encourage fishermen to
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split trawls or strings, thus increasing
the number of vertical lines in the water
column. In addition, requiring one buoy
line may increase the risk of gear loss,
thereby increasing the entanglement
risks associated with ‘‘ghost gear’’ or
fishing gear left untended or lost that
continues to fish. Therefore, this would
not be an effective broad-based measure
to implement. NMFS will work with the
ALWTRT to address the risk associated
with vertical lines through future
rulemaking.
Comment 209: Several commenters
prefer the single buoy line requirement
in SAM. One commenter stated that this
would decrease the number of buoy
lines in the water, which offsets the
amount of ghost gear created from gear
lost due to weather, gear conflicts, etc.
Another commenter suggested using one
buoy line in Cape Cod Bay, Great South
Channel, Stellwagen Bank/Jeffreys
Ledge, other Northeast gillnet waters,
SAM, Mid-Atlantic Coastal waters, and
other Southeast gillnet waters.
Response: As noted in Comment 208,
neither the ALWTRT nor NMFS is able
to identify a viable option for further
reducing the risk associated with
vertical lines at this time. NMFS has
concluded that allowing the use of two
buoys in SAM areas as specified in this
final action will not result in an increase
in the amount of vertical line in the
water. NMFS will work with the
ALWTRT to address the risk associated
with vertical lines through future
rulemaking.
Comment 210: Many commenters
supported the use of two buoy lines for
the following reasons: (1) It would
reduce the number of buoy lines in the
area; (2) it would make gear easier to
grapple; (3) it would help reduce gear
loss/ghost gear; and (4) it would provide
for safer hauling conditions.
Response: NMFS supports and allows
the use of more than one buoy line.
However, NMFS notes that Cape Cod
Bay (January 1—May 15), Northern
Nearshore Lobster Waters, Stellwagen
Bank/Jeffreys Ledge Restricted Area,
and Cape Cod Bay Restricted Area
(Federal Waters May 16–December 31)
currently have minimum limits on the
number of traps per one buoy line. See
response to Comment 208.
Comment 211: Many commenters
supported 2 buoy lines for trawls of 5
or more traps.
Response: NMFS agrees with the
commenters that 2 buoy lines are
needed for many fixed gear fisheries.
However, see response to Comment 208.
NMFS notes that Cape Cod Bay (January
1–May 15), Northern Nearshore Lobster
Waters, Stellwagen Bank/Jeffreys Ledge
Restricted Area, and Cape Cod Bay
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Restricted Area (Federal Waters May
16–December 31) currently have
minimum limits on the number of traps
per one buoy line. See response to
Comment 213.
Comment 212: One commenter
supports a second buoy line in SAM.
The commenter believes this will cut
the overall numbers of buoys in SAM.
Currently, most people have 2–3 traps
on a buoy line because the traps are too
expensive to risk setting more on a
single buoy line. Thus, if NMFS allowed
a second buoy line, there would be
fewer small sets of gear and less buoys,
and the risk for gear loss would also be
reduced.
Response: As discussed in the
response to Comment 209, the use of
two buoy lines is allowed in SAM areas
through this final action. Additionally,
see response to Comment 211 for a
reminder of the areas where minimum
limits on the number of traps per one
buoy line are required.
Comment 213: Several commenters
did not support the use of one buoy line
per trawl of 4 or fewer traps. The
commenters state that this may cause
fishermen to shorten trawl lengths and/
or split their trap trawls to minimize
losses and maintain the current number
of traps in use. This may then cause an
increase in the number of buoy lines in
the water column.
Response: NMFS will further address
issues related to serious injury and
mortality due to vertical lines through
future rulemaking. In regard to the
number of buoys per trawl allowed, this
final action will maintain the status quo
(i.e., one buoy line per trawl of five or
less traps) for the various management
areas that were under consideration.
Therefore, NMFS is rejecting the
alternative considered in the DEIS that
allows the use of one buoy line per
trawl of 4 or less traps. NMFS
recognizes the concern raised by the
commenters that some individuals may
shorten trawl lengths, thereby resulting
in additional buoy lines being deployed
under the current management regime.
As noted, NMFS intends to work with
the ALWTRT to address the risk
associated with vertical lines through
future rulemaking.
Comment 214: Some commenters
believe there is no justifiable basis for
allowing two buoy lines (other than to
avoid gear loss).
Response: NMFS has received reports
indicating that allowing only one buoy
line may cause some fishermen to split
their trawls and fish shorter trawls,
which can result in the same or a greater
number of buoy lines. In addition,
requiring fishermen who traditionally
fished longer trawls with two buoys to
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use a single may present a safety hazard
for fishermen. Having a single buoy
dictates the direction from which
fishermen can haul/retrieve their gear.
Depending on the sea state, this may
place the crew and vessel in harm’s way
if the vessel is not in the preferred and/
or more stable hauling position. Having
the choice to start a haul from either end
of a string allows fishermen to choose
the safest and most stable vessel
direction relative to wind and sea
conditions. In addition, the use of a
second buoy line on trawls/strings of
gear could provide a platform for
continued testing of new buoy line
modifications designed to address the
threat of vertical line entanglements.
Several potential gear modifications that
offer opportunities to reduce the serious
injury and mortality due to vertical lines
are under investigation (e.g., Time
Tension Line Cutter (TTLC), acoustic
pop-up buoys, the use of buoy line
retrieval line or tag line (made from line
with a reduced breaking strength)
marking the gear’s position, acoustic
hauling/release links and galvanic timed
release devices).
Comment 215: One commenter states
that one buoy line for four or fewer traps
is less restrictive than one buoy line for
five or fewer and this will increase the
number of buoy lines in the water
column, which represents a relaxation
of the current requirement. Further, the
commenter states there is no way to
measure the benefits of relaxing this
requirement.
Response: As discussed in the
response to Comment 213, this action
will maintain the status quo (i.e., one
buoy line per trawl of five or less traps)
thereby rejecting the alternative
considered in the DEIS that allows the
use of one buoy line per trawl of four
or less in certain management areas.
Comment 216: Two commenters said
NMFS should minimize the number of
knots in buoy lines or require knot-free
buoy lines.
Response: NMFS currently
encourages, but does not require,
fishermen to maintain knot-free buoy
lines. While splices are considered less
of an entanglement threat and are
preferable to knots, NMFS recognizes
that such a requirement is not practical,
has safety concerns, etc. However,
NMFS has encouraged the development
of a device that makes knotless
connections. If such a device is
developed in the future, NMFS will
revisit the issue at that time.
Comment 217: Several commenters
support allowing 1⁄3 poly on the bottom
of buoy lines.
Response: Through this final action,
fishermen have the option to use buoy
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lines with the bottom 1⁄3 of the line
composed of floating line within SAM
areas and Cape Cod Bay during the
restricted time periods. The remainder
of the line must be composed of sinking
and/or neutrally buoyant line. Outside
of SAM areas and Cape Cod Bay,
fishermen have the option to utilize
buoy lines composed of what ever type
of rope they choose as long as no buoy
line is floating at the surface. Following
12 months after publication of this final
rule, fishermen will have the option to
utilize the type of buoy line they choose
to use in current SAM areas, again, as
long as no buoy line is floating at the
surface.
Comment 218: Two commenters
requested to use more floating line in
buoy line than what was proposed. One
commenter stated that if fishing in 50
fathoms (91.4 m or 300 ft) of water,
fishermen need more because if they use
sinking line, the tide will take down the
buoy, but if they use more floating line
then they can use less buoy line. The
commenter said that floating line helps
keep the line on the surface and that
they need more than 2⁄3 floating line in
heavy tides. Another commenter said he
uses 1⁄2 to 2⁄3 floating line in his buoy
line. Also, if he was required to only use
1⁄3 poly at the bottom, he would have to
use toggles, which are a safety hazard to
fishermen.
Response: As discussed in the
response to Comment 217, outside SAM
areas and Cape Cod Bay, fishermen have
the option of utilizing the type of buoy
line they choose as long as there is no
buoy line floating on the surface. The
option to use buoy lines with the bottom
1⁄3 of the line composed of floating line
applies only to the SAM areas and Cape
Cod Bay during the restricted time
periods and is not one of the broadbased measures implemented by this
final action. Following 12 months after
publication of the final rule, fishermen
will have the option to utilize the type
of buoy line they choose to use in
current SAM areas as long as no buoy
line is floating at the surface.
Comment 219: One commenter said
that floating rope does not float on the
surface of the water like NMFS thinks
it is.
Response: NMFS recognizes that a
number of factors may affect the profile
of buoy line and groundline in the
water, including tide and current. In the
case of groundline, underwater video
recordings of typical trap/pot gear with
floating groundline between traps
revealed that the line often forms large
loops in the water column between
traps. While there is currently no
definition for ‘‘floating rope’’, this final
rule provides definitions of ‘‘neutrally
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buoyant line’’ and ‘‘sinking line’’ (see
section 229.2). Under the ALWTRP,
buoy line floating at the surface is
universally prohibited.
Comment 220: One commenter states
that the use of neutrally buoyant line
has not been proven for buoy lines in all
conditions.
Response: Presently, fishermen use
neutrally buoyant line for buoy line in
active fishing operations. In addition, a
recent modeling study conducted by the
Massachusetts Department of Marine
Fisheries compared the profiles of buoy
lines of different proportions of floating,
sinking and neutrally buoyant rope
under a variety of currents. The
modeling results indicate that, except
for at all but the lowest of currents, buoy
lines showed similar profiles regardless
of line composition (i.e., sink, float,
neutrally buoyant). Finally, it is known
that fishermen have experimented with
neutrally buoyant rope as buoy lines
since the late 1990s and continue to use
it.
Comment 221: One commenter states
that the bottom 1⁄3 floating line on buoy
lines should be allowed in SAM. He
also stated that flume experiments
showed that leaving the bottom 1⁄3 as
floating line did not pose a problem to
the whales and also prevented the traps
from ‘‘rocking down’’ (i.e., hanging
down). He states that floating
groundline is the cause of most
entanglements, and that there is more
groundline in the ocean than buoy line,
thus groundline should be regulated
more than buoy line.
Response: See response to Comment
217.
Comment 222: One commenter states
that a clip is needed to take buoys off
the line.
Response: Clips to facilitate removal
of buoys are not prohibited as long as
they are located above the strong end of
the weak link in the buoy line.
Comment 223: One commenter states
that, for vertical line in 30 feet (9.1 m)
water, there are 150 feet (45.7 m) of
vertical line. In the bay with less
current, any sinking rope has a tendency
to get wrapped around the anchor.
Response: See response to Comment
217.
Comment 224: One commenter said
that, if sinking vertical lines are
required, people are going to use toggles
and they are going to tie or snap-on
toggles to the vertical line. These toggles
will keep rope straight up, which is
going to produce more stuff for whales
to drag around.
Response: See response to Comment
217.
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Comment 225: One commenter said
that no options were considered other
than weak links.
Response: In addition to weak links,
a number of options to reduce the risk
of serious injury and mortality due to
vertical lines have been considered.
While the alternatives considered in this
proposed rule focus primarily on
reducing risks associated with
groundlines, NMFS is responding to the
vertical line issue through such
measures as expanded gear marking,
reducing the breaking strength of weak
links, regulating additional fisheries
under the ALWTRP, and considering
two buoy lines allowed per trawl or
string. As a result, NMFS is outlining a
strategy to reduce interactions with
groundlines in this final rule, along with
some measures to address vertical lines,
and plans to further address the risk
associated with vertical lines through
future rulemaking. In addition, research
into reducing the risk associated with
vertical line is ongoing. This research is
focusing on the profiles of vertical line
with different buoy line configurations
(e.g., sinking and/or neutrally buoyant
vs. polypropylene), as well as other
modifications (e.g., requiring a
minimum number of traps per trawl in
certain areas). NMFS and others are also
investigating how whales utilize the
water column, including foraging
ecology and diving behavior, which will
help determine the appropriate
mitigation strategies for reducing
entanglement risk from vertical lines.
Comment 226: One commenter stated
that fishermen use a knot in the middle
attached to a buoy to keep sinking line
off the bottom and asked that we not
eliminate buoy line with 2⁄3 sinking line
on top spliced to 1⁄3 floating line on the
bottom, which is more whale-friendly.
Response: NMFS currently
encourages, but does not require,
fishermen to maintain knot-free buoy
lines. See response to Comment 217.
Comments on Gillnets
Comment 227: One commenter cannot
see how gillnets can ever be modified
such that they are risk-free to whales,
unless a pinger modification is found
that works with no adverse effects.
Response: NMFS believes that the
required gear modifications will prevent
entanglements where possible and
reduce the severity of entanglements
due to gillnet gear and will reduce the
risk of serious injury or mortality. At
this time, NMFS does not believe that
Acoustic Deterrent Devices (ADDs or
pingers) and Acoustic Harassment
Devices (AHDs) are an appropriate
measure to reduce interactions with
large whales. ADDs (or pingers) and
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AHDs are audible alarm devices which
warn small cetaceans and pinnipeds
away from commercial fishing gear and
aquaculture operations by emitting
sound pulses. No evidence exists that
large whales would, in fact, respond to
such a sound signal. In addition,
exposure to alarm or alerting stimuli
may result in whales abandoning a
desired feeding or mating area, which
could result in significant adverse
effects on the population. Finally, ADDs
typically operate at much higher
frequencies (e.g., about 12 kHz) than
right whales generally hear and vocalize
(e.g., less than 4 kHz).
Comment 228: One commenter
suggested that NMFS implement gillnet
measures year-round everywhere,
including the Southeast.
Response: The potential for
entanglement of whales in the south and
Mid-Atlantic waters during summer
months is minor. Therefore, the yearround requirements offer only minimal
risk reduction compared to the seasonal
requirements provided in this final rule,
which are based on the movement and
sightings of whales.
Comment 229: One commenter urged
NMFS to prohibit gillnets from
Stellwagen Bank National Marine
Sanctuary.
Response: See response to Comment
16.
Comment 230: NMFS received one
comment in support of the 22-lb (10-kg)
Danforth-style anchor.
Response: NMFS agrees that the 22-lb
(10-kg) Danforth-style anchor is
appropriate based on research and
testing and has implemented this
provision in this final rule.
Comment 231: One commenter
opposed the anchoring requirement for
‘‘stab nets’’ in the Mid-Atlantic.
Response: In Mid-Atlantic gillnet
waters, the anchoring requirement is
only in effect when anchored gillnets do
not return to port with the vessel.
Therefore, this final rule does not
contain an anchoring requirement for
stab nets returned to port with the
vessel.
Comment 232: Several commenters
cautioned that many of the proposed
gear modifications (e.g., the use of
sinking line, weak links and 22-lb (10.0kg) Danforth anchors) pose considerable
safety risks to fishermen. These
commenters advised that sinking line
will snag on jagged bottom surfaces,
weak links could snap during hauls, and
Danforth anchors will be dangerous to
retrieve in rough seas. One commenter
also stated that the difficulty of
retrieving Danforth anchors in adverse
conditions will lead to more anchors
being left on the bottom and force
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fishermen to buy already-expensive
replacement anchors more often.
Response: Safety issues are always a
concern to NMFS. NMFS believes that
the gear modifications required under
the ALWTRP do not present significant
increased dangers above those of normal
fishing practices. However, NMFS will
continue to monitor this situation
through discussions with industry and
the ALWTRT. All three modifications
stated by the commenters were tested in
the Northeast, Mid-Atlantic, and
Southeast regions under diverse weather
conditions and were found to be
successful. Although NMFS tested
Danforth-style anchors in unfavorable
weather conditions, fishermen should
contact the NMFS Gear Research Team
if they experience problems. This final
rule states that gear has to be anchored
at each end of the net string with an
anchor that has the holding power of at
least a 22-lb (10.0-kg) Danforth-style
anchor, not necessarily a Danforth
anchor. However, fishermen in the MidAtlantic and Southeast do not have an
anchoring requirement unless they
return to port without their gear.
Additionally, NMFS is approving a
weak link anchoring option for gillnet
fisherman within 300 yards (274.3 m or
900 ft) of the beach in North Carolina to
alleviate safety issues in this area.
NMFS gear specialists are available to
consult on these issues and to provide
suggestions on how to comply with this
requirement. In response to any safety
risks posed by weak links, gear research
studies that involved pulling a string of
nets in the Gulf of Maine in up to 45
knots (51.8 mi/hr or 83.3 km/hr) of wind
in 100 fathoms (182.9 m or 600 ft) of
water and utilizing 1,100-lb (272.4-kg)
weak links resulted in no failures. Thus,
NMFS believes that it is unlikely that
the weak links in the gillnets would
break during fishing operations. The
NMFS Gear Research Team will
continue to investigate weak links and
various anchoring systems. Regarding
safety issues related to sinking line, see
response to Comment 128.
Comment 233: Two commenters do
not support an 1,100-lb (499-kg) weak
link for driftnets fished at night. They
state that nets are 50–60 ft (15.2–18.3 m)
deep, are not strong enough, catch fish
like bluefish and albacore, and can
break easily and create ghost gear if
weak links are required. The fishery is
from May to July. They state that there
has been observer coverage the last 4 yrs
(36 trips) and no entanglements were
observed.
Response: NMFS is not implementing
the proposed weak link requirement for
tended driftnet gear at this time due to
potential safety issues that were raised.
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Thus, NMFS believes further research
on this fishery, and specifically testing
weak links in drift gillnet gear, is
needed before weak links should be
required. NMFS will conduct research
in this fishery and discuss whether
additional requirements are warranted
with the ALWTRT. NMFS
acknowledges that few interactions
between large whales and commercial
fisheries have been observed and
recorded by NMFS observers. These are
rare events; however, they are occurring
at a rate unsustainable for the large
whale populations covered by the
ALWTRP.
Comment 234: One commenter
encouraged NMFS to require 600-lb
(272.2-kg) weak links on all flotation
devices attached to the buoy line of
driftnet gear.
Response: Driftnet gear will have
requirements under this final rule;
however, buoy line weak links will not
be required. NMFS will discuss whether
additional restrictions are warranted for
the driftnet fishery with the ALWTRT.
Comment 235: Several commenters
were concerned about the current
requirement that driftnets be attached to
the boat at all times at night. The
commenters stated that certain types of
driftnets used in the Mid-Atlantic region
would not fish properly if the net is
constantly attached to the boat.
Response: Presently, this requirement
applies in the Mid-Atlantic from
December to March under the ALWTRP.
This final rule extends this requirement
from September to May. NMFS will
raise this issue for further discussion
with the ALWTRT at future meetings.
However, at this time, NMFS is not
aware of driftnet fisheries that release
the net from the vessel at night.
Comments Specific to Certain Fisheries/
Additional Fisheries Under the
ALWTRP
Comment 236: One commenter states
that testing is needed on the beach seine
fishery, which is a selective type of
fishing.
Response: At this time, NMFS is not
regulating gillnets that are anchored to
the beach and subsequently hauled onto
the beach to retrieve the catch. This
fishing technique is known to occur on
the beaches of North Carolina. NMFS
will be discussing what the appropriate
management measures for this unique
fishery should be with the ALWTRT at
a future meeting. In the meantime,
NMFS will conduct outreach and
research on this fishery to support
future discussions with the ALWTRT.
NMFS will be coordinating with the
North Carolina Department of Marine
Fisheries to revise the definition for
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beach-based gear to help ensure
landings are reported accurately for
beach-based gear versus gillnets, among
other issues.
Comment 237: Several commenters
state that recreational fisheries are
currently not covered under the plan
and should be regulated under the
ALWTRP and, in some areas, such as
southern New England, they comprise a
great deal of fixed gear. One commenter
states that all fixed gear, whether it be
from recreational or commercial
fisheries, should be regulated similarly.
Response: NMFS appreciates the
concerns raised by the commenter and
reiterates that NMFS currently issues
regulations to reduce marine mammal
serious injuries and mortalities during
commercial fishing operations as
mandated by MMPA section 118. The
MMPA does not currently authorize the
Secretary to address marine mammal
bycatch from non-commercial fisheries.
However, recreational fishers that take
marine mammals are in violation of the
MMPA prohibition against taking
marine mammals. NMFS has created
brochures designed to inform
recreational fishermen about protected
species conservation.
Comment 238: One commenter
requested that NMFS consider
regulations that prohibit recreational
boats from leaving vessel anchoring
systems to occupy a fishing spot
without actually fishing there. The
commenter believes recreational vessels
should be prohibited from tying up to
fixed gear high flyers because it is
doubtful that a 1,500-lb (680.4-kg) weak
link would hold a recreational vessel.
The commenter believes this practice
increases gear loss in the Mid-Atlantic.
Response: See response to Comment
237 for legal authorization to regulate
recreational fisheries. See also response
to Comment 190 regarding vessels tying
onto other vessels’ line. It is unlawful,
however, for any person to steal or
attempt to steal or to negligently and
without authorization remove, damage,
or tamper with fishing gear owned by
another person located in the EEZ.
Comment 239: Several commenters
urged NMFS to investigate emerging
fisheries (e.g., whiting fishery and
octopus fishery in Florida) that could
use fishing gear that poses a threat to
whales.
Response: NMFS currently publishes
the Atlantic Ocean, Gulf of Mexico, and
Caribbean Category I & II List of
Fisheries under the Marine Mammal
Authorization Program (MMAP) and
includes both state and Federal waters.
In addition to the current list of fisheries
managed by NMFS, any new or
emerging fishery operating in Federal
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waters that are federally managed is
subject to section 7 consultation under
the ESA. NMFS also works closely with
the fishing industry, state management
agencies and any interested partner as
part of the ALWTRT to understand any
new and emerging fisheries that may
present a risk to large whales.
Comment 240: One commenter
understands incorporating other
fisheries in addition to those already
subject to the ALWTRP, but pot
fisheries such as scup, black sea bass,
and conch occur early summer to fall,
and the commenter believes right
whales are unlikely to reside in waters
where and when this gear is fished. The
commenter requested that NMFS
examine sightings and exempt Rhode
Island state waters. Another commenter
wonders about risk reduction from
adding in smaller fisheries like black sea
bass and scup. The commenter believed
that the risk reduction may be minimal
and duplicative.
Response: NMFS established the areas
and seasons being implemented in this
final rule by analyzing databases that
included right, humpback, and fin
whale sightings. The areas included in
the final rule are, amongst other factors,
those where documented large whale
sightings are common. NMFS believes
that the final rule has an appropriate
suite of conservation measures to
minimize entanglements resulting in
serious injury or mortality to large
whales.
It is true that few scup and black sea
bass vessels operate relative to other
trap/pot fisheries, such as the lobster
fishery. However, over 400 vessels are
permitted for black sea bass trap/pot in
the northern fishery and over 300
vessels are permitted for scup trap/pot.
Harvest data also suggest that southern
vessels seek black sea bass as a principal
or secondary target species. Therefore,
the amount of gear associated with these
fisheries is significant. The addition of
these fisheries to the ALWTRP is
equitable given that the gear and
geographic distribution of effort are
similar to the lobster fishery.
Comment 241: One commenter
believes that risk reduction is greatest
from adding in the hagfish fishery. Also,
the commenter states that other fisheries
added in do not have the same amount
of effort, but that adding them should
provide some benefit.
Response: The available data do not
allow NMFS to characterize definitively
the risk (or risk reduction) associated
with individual fisheries, particularly
smaller fisheries such as hagfish for
which permit data are lacking. New
fisheries are being added in to address
their contribution to entanglement risk,
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and because of the similarity between
their gear and the gear of currently
regulated fisheries.
Comment 242: Some commenters
believed that traps for black sea bass
and snapper in the Mid-Atlantic region
should be exempt from the regulations
since these traps are usually hauled to
port every night and therefore cause a
minimal risk of whale entanglement.
Response: NMFS recognizes that any
line in the ocean poses some risk of
entanglement and believes that this final
rule has an appropriate combination of
conservation measures to minimize
entanglements resulting in serious
injury or mortality to large whales.
Comment 243: When implementing
this final rule, one commenter asked
NMFS to consider local New Jersey
fishing practices and regional fishery
conditions. For example, the commenter
stated that many vessels are from the
same port, there are no more than 30
vessels, and all vessels fish in close
proximity to each other. The commenter
also stated that there is significant
communication among vessel operators
if whales are present.
Response: NMFS recognizes that there
are regional issues that influence fishing
techniques. This final rule represents a
broad-based management scheme;
however, regional differences were
considered when developing the final
rule in consultation with the ALWTRT,
which has members from Regional
FMCs, coastal state fisheries that
interact with large whale species or
stocks protected under the ALWTRP,
interstate fisheries commissions,
academic and scientific organizations,
environmental groups, and other
interested stakeholders. NMFS believes
that the final rule has an appropriate
suite of conservation measures to
minimize entanglements resulting in
serious injury and mortality to large
whales. NMFS will continue to discuss
regional differences with the ALWTRT
when considering future management
measures.
Comment 244: One commenter stated
that there are only two full time pot
fishermen in Virginia Beach and two in
Chincoteague. Unless there is a problem
in the area, the fishermen should not be
economically impacted, especially since
the commenter states there are no
whales in the area. Until there is more
data showing that the mid-Atlantic is an
important area for whales, regulations
should not change.
Response: The ALWTRP was
developed to reduce the level of serious
injury and mortality of North Atlantic
right, humpback, and fin whales. NMFS
data indicate that there have been
multiple sightings of right whales in the
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nearshore area of the Delmarva
Peninsula (mostly between March–
May), and humpback and fin whales are
also present in the area seasonally.
Thus, NMFS believes that action is
appropriate in this area. Fixed gear
fisheries have been documented to
entangle large whales and the location
where the gear was deployed is not
always known. Based on NMFS gear
analysis reports, between 1997 and 2003
there were 36 confirmed entanglements
between large whales and pot fishery
gear. Also see response to Comment 243
regarding regional differences.
Comment 245: Numerous commenters
objected to the proposed gillnet
regulations for North Carolina fisheries.
A few commenters stated that the
fishery in North Carolina is different
than that farther north. One commenter
stated that a 22-lb (10.0-kg) Danforth
anchor is not needed in North Carolina,
as no whales have been sighted close to
the beach. Another commenter stated
that the 22-lb (10.0-kg) anchors should
not be required inside 3 nautical miles
(5.6 km). Instead of the proposed
regulations, several commenters
recommend that North Carolina
fisheries that target spot in the fall and
sea mullet and weakfish in the spring
and operate out to 300 yards (274.3 m
or 900 ft) be allowed to use dead
weights on the inshore end and anchors
less than 22-lb (10.0-kg) Danforths on
the offshore end, and allow 600-lb
(272.2-kg) weak links. Commenters state
that these changes are necessary for the
following reasons: (1) the nets are short
(150–200 yards (137.2 m–182.9 m or 450
ft–600 ft)) with small webbing (<3 in.
(0.1 m) stretched); (2) the nets are fished
close to the beach using boats 16–25 ft
(4.9–7.6 m); (3) the nets are set late in
evening and fished in early morning;
and (4) there are safety issues with
requiring any type of anchor on the
inshore end.
Response: NMFS agrees that an
additional anchoring and weak link
option is appropriate for vessels
operating within 300 yards (274.3 m or
900 ft) of the beach in North Carolina.
The Mid/South Atlantic ALWTRT
Subgroup agreed by consensus to an
optional configuration for these
fisheries. The gear requirements for
gillnet gear set within 300 yards (274.3
m or 900 ft) of the coast in North
Carolina will have an optional
configuration: five or more weak links
per net panel, depending on panel
length, with a breaking strength no
greater than 600 lbs (272.2 kg), to be
anchored with the holding power of at
least an 8-lb (3.6-kg) Danforth-style
anchor on the offshore end of the string
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and a 31-lb (14.1-kg) dead weight on the
inshore end of the net string.
NMFS believes that the gear
modifications required under the
ALWTRP do not present significant
additional dangers above those of
normal fishing practices. However,
NMFS will continue to monitor this
situation through discussions with
industry and the ALWTRT.
NMFS disagrees with the comment
that there have been no whales seen
close to the beach in North Carolina.
Sightings data in the NARW Sightings
Database show that there have been
numerous right whale sightings
throughout the Mid-Atlantic within 1
nautical mile (1.9 km) of the beach.
Further, of 413 Mid-Atlantic right whale
sightings in the NARW Sightings
Database, over 200 were within 5
nautical miles (9.3 km) of the beach.
Comment 246: Many commenters
expressed a concern for safety with the
proposed gillnet regulations in North
Carolina. Several commenters stated
that the regulations would have the
potential for loss of life and gear. One
commenter stated that dead weights are
needed in case there is increased wind
or rough surf, so the net can be pulled
into safer waters for retrieval (tough to
retrieve an anchor in these conditions).
Fishermen are typically within 200
yards (182.9 m or 600 ft) of the surf
zone. The commenter stated that, if the
proposed requirement is implemented,
fishermen may stop fishing, leave their
nets in the water until surf conditions
subside, and risk losing gear and/or
catch. One commenter states fishermen
may also be forced to ignore the safety
hazards and retrieve the anchor from
rough water. A few commenters state
that the 22-lb (10.0-kg) Danforth anchor
on the inshore end is a safety risk
because it is impossible to remove in the
surf zone. However, they state that a 22lb (10.0-kg) Danforth anchor can be used
offshore at 200 yards (182.9 m or 600 ft).
Response: See response to Comment
245.
Comment 247: One commenter
believes that the 22-lb (10.0-kg)
Danforth anchor requirement is a
problem on the inshore end of the string
for North Carolina and Virginia, where
fishing occurs for sea mullet and pan
trout in the spring. However, the
commenter states that a dead weight
would be okay to use.
Response: See response to Comment
245. This final rule does not contain an
optional anchoring configuration within
300 yards (274.3 m or 900 ft) of the
beach in Virginia. However, NMFS will
discuss whether this option should be
extended to other areas with the
ALWTRT at the next meeting.
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Comment 248: One commenter stated
that a 13-lb (5.9-kg) Danforth anchor is
used with a 3-foot (0.9-m) chain or 25lb (11.3-kg) Navy anchor on the offshore
end and 40-lb (18.1-kg) lead weights on
the inshore end. The commenter further
stated that the net can get dragged
offshore if conditions are bad. The
commenter would be willing to use a
22-lb (10.0-kg) Danforth anchor on the
offshore end along with weak links to
make his gear whale-safe.
Response: See responses to Comments
245 and 247.
Comment 249: One commenter
believes that the 22-lb (10.0-kg)
Danforth anchor provision is a problem
both inshore and offshore. According to
the commenter, especially in
September, fishermen fish close to the
beach and haul from the bow, and
pulling that anchor could cause the boat
to capsize in small waves. The
commenter recommends using a dead
weight inshore and an 8-lb (3.6-kg)
Danforth anchor offshore.
Response: See response to Comment
245.
Comment 250: One commenter
suggested that NMFS not change the
seasonal window from December–
March 31 to September 1–May 31. If
NMFS changes the time period, the
commenter requested that the inshore
small mesh fishery (<5 in (0.1 m), 300
yd (274.3 m or 900 ft) max. set) use a
dead weight inshore and an 8-lb (3.6-kg)
Danforth anchor offshore end and 600lb (272.2-kg) weak links rather than
1,100 lb (499 kg) weak links.
Response: NMFS has analyzed the
NARW Sightings Database through early
2003, supplemented by additional data
on humpback and fin whale sightings,
including both opportunistic and
systematic survey data. The associated
time frames of conservation measures
included in this final rule are times
where documented large whale
sightings primarily occur. Thus, NMFS
believes the September 1–March 31
window is appropriate for the MidAtlantic.
With respect to the use of various
anchoring systems, please see responses
to Comments 245 and 247.
Comment 251: One commenter has a
problem fishing anytime or anywhere
using a 22-lb (10.0-kg) anchor. The
commenter states that smaller boats do
not have enough room for the anchors
and it is unsafe to have them. The
commenter supports using a 13-lb (5.9kg) anchor instead.
Response: NMFS agrees and has
changed the anchoring requirements for
smaller vessels operating within 300
yards (900 ft or 274.3 m) of the shoreline
in North Carolina [see Changes From the
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Proposed Rule section]. See responses to
Comments 245 and 247.
Comment 252: One commenter states
that the proposed regulatory actions, if
not modified, would be inconsistent
with enforceable North Carolina
Administrative Code 15 A NCAC
07H.0207 and will have an effect on
Public Trust Areas and Estuarine
Waters. The commenter states that, if
the proposed measures are not
modified, they would adversely affect
the public’s ability to conduct
recreational and/or commercial fishing.
The commenter supports DEIS
Alternative 3 conditioned on
modifications (below), concurrent with
North Carolina’s CZMA program. North
Carolina proposes that the fishing
season and time period required for the
Mid/South Atlantic region remain
unchanged. If the time period is
changed, the state believes that an
alternative configuration be considered
as the expansion of the gear restricted
period and the requirement for
fishermen to use Danforth-style anchors
during this period may create safety
hazards for coastal fishermen setting
nets in the coastal zone during the early
fall/late spring. The State also requests
that NMFS reconsider the mandatory
use of sinking and/or neutrally buoyant
line (and/or offer low cost alternatives)
and extend the effective date to January
1, 2010, to reduce potential economic
hardship and increase the time available
to replace current gear. Finally, the State
does not support the alternative marking
system for fishermen who use gear in
both Mid-Atlantic and Northeast waters,
believing that this system would cause
a financial burden on fishermen as they
would have to buy another set of buoy
lines for this gear. The State instead
proposes a unique, individual marking
system like the one currently being
evaluated by Dr. Harper with the
Virginia Sea Grant Marine Advisory
Program. If these conditions are not met,
then the State would object to the
proposed rule.
Response: NMFS based the
components of the final rule on
numerous discussions with the
ALWTRT. NMFS believes that the final
rule has an appropriate combination of
conservation measures to minimize
entanglements resulting in serious
injury and mortality to large whales.
Through this action, NMFS will
finalize an expanded season in the midAtlantic when ALWTRP requirements
are effective (see response to Comment
151). Also, see the response to Comment
245 for gear requirements, anchoring
options and safety considerations. With
respect to the implementation schedule
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for the groundline requirements, see
response to Comment 118.
NMFS reiterates that the gear marking
requirements in this final rule only
require buoy lines to utilize one 4-inch
(10.2-cm) colored mark midway on the
buoy line. A possible option for meeting
this requirement is weaving the
appropriate color marking into the buoy
line. NMFS will continue to discuss
gear marking strategies with the
ALWTRT and support research and
development of promising marking
technologies.
Comment 253: One commenter said
that there is no problem with whale
interaction and gillnet gear off the North
Carolina coast. Several commenters
wanted to know if the 1,100-lb (499.0kg) weak link has been tested off North
Carolina in fisheries where they fish
from 5 fathoms (9.1 m or 30 ft) to 70
fathoms (128 m or 420 ft) and
questioned what the effects are on the
nets. The commenter believes that their
fisheries are being grouped with others,
when one size does not fit all.
Response: While it is often difficult to
identify the specific gear type involved
in an entanglement, NMFS has evidence
that fixed gear types, such as gillnets,
have entangled large whales. Thus, it is
necessary to regulate all fisheries that
use this gear to ensure protection of
whales. Based on NMFS gear analysis
reports from 1997 to 2003, there were 23
confirmed entanglements preliminarily
attributed to gillnet gear; these events
involved 2 right whales, 18 humpback
whales, 2 fin whales, and 1 minke
whale. Of those 23, 6 were
entanglements involving gillnet gear
that were first sighted off the coast of
North Carolina.
Testing of weak links has occurred
and continues to be conducted by
NMFS gear specialists and NMFS
believes that weak links are a valuable
tool to minimize risk to large whales.
Comment 254: One commenter
provided NMFS with a description of
the North Carolina black sea bass
fishery. Specifically, North Carolina
fishers use smaller pots than those from
Virginia northward; approximately half
of the NC fishers use groundline and
fish overnight sets; the rest use singles,
fewer pots, and do not leave them in the
water overnight. Further, depending on
the number of pots, fishers will fish up
to 3 times a day, usually using short
groundlines (<30 ft (9.1 m)). The
commenter suggested that NMFS
consider requiring North Carolina black
sea bass fishermen to use lower profile
lines, which could be created at
relatively low cost by weaving lead into
poly lines, and would keep lines
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approximately 2 ft (0.6 m) off the
bottom.
Response: The gear requirements in
this final rule state that Mid-Atlantic pot
fishery gear, including black sea bass
gear is regulated similar to lobster trap
gear, and is subject to sinking and/or
neutrally buoyant groundline
requirements 12 months after
publication of this final rule. See the
response to Comment 158 with regard to
low profile line, and the response to
Comments 243 and 255 with regard to
regional issues.
Comment 255: One commenter was
concerned about sinking line between
pots. The commenter said that the bass
pot fishery in the Mid-Atlantic and the
lobster pot fishery in the northeast (pots
100 feet (30.5 m) apart) are very
different. The commenter said that,
down south, they fish on bottom
structures with pots 10–12 feet (3.0–3.7
m) apart with 8 pots per buoy.
Response: See response to Comment
243 regarding regional issues. Floating
line between traps has been implicated
in large whale entanglements; NMFS
has evidence that establishes the risk
associated with this gear configuration.
Underwater video footage of typical
lobster gear with floating groundline
shows that it forms large loops in the
water column between traps. Similar
underwater video footage of neutrally
buoyant line between traps indicated
that it did not have the same vertical
profile as floating line; rather, it was
located on or near the bottom, thus
reducing the risk of entangling a large
whale. Therefore, NMFS expects that by
eliminating most floating line and
requiring sinking and/or neutrally
buoyant groundline in the pot fisheries
will remove a large percentage of the
line in the water column.
Comment 256: A few commenters
agreed that the red crab fishery should
be exempt from regulations at depths
greater than 280 fathoms (512.1 m or
1,680 ft).
Response: NMFS appreciates the
comment and the support for the final
rule.
Comment 257: Several commenters
raised a habitat issue with using
sinking/neutrally buoyant groundline.
Specifically, the commenters stated that,
in the snapper/grouper fishery, there are
regulations prohibiting roller-rig trawls
and traps for any species other than
black sea bass to reduce habitat impacts.
Additionally, there are closed areas to
protect Oculina coral.
Response: See response to Comment
128.
Comment 258: One commenter stated
that the hagfish fishery is much smaller
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than the lobster fishery and therefore
poses less risk than lobster gear.
Response: NMFS acknowledges that
the hagfish fishery currently represents
a small percentage of fixed gear
compared to the lobster fishery.
Although the hagfish fishery is a
relatively smaller fishery, its gear has
been documented to have entangled
large whales.
Comment 259: One commenter stated
that when the Great South Channel is
closed from April 1–June 30, fishers
move around to areas closed to draggers,
which means they go to the Georges
Bank Closure in May and then Closed
Area 1 in June. The commenter further
states that hagfish are abundant during
these times in these areas, possibly the
most productive months of the year. The
commenter believes that closing this
area at these times would have
devastating effects on this fishery.
Response: NMFS acknowledges and
appreciates the concerns raised by the
commenter. NMFS will treat other pot
fisheries similar to the lobster fishery in
this final rule, so the hagfish fishery will
be subject to regulations to reduce the
risk to endangered and threatened large
whale stocks.
Comment 260: One commenter states
that, by adding the hagfish fishery to the
group of fisheries subject to the
ALWTRP, it would be regulated like the
lobster fishery. The commenter states
there are differences that should be
considered, such as weight of the traps
(300–500 lbs. (136.1–226.8 kg)) when
full, frequency of hauling the gear (every
12–18 hours), consideration of
historically fished areas (like Great
South Channel critical habitat), and the
size of the hagfish fishery (smaller than
the lobster fishery).
Response: NMFS believes it is
appropriate to regulate the hagfish
fishery similar to the lobster trap/pot
fishery under the ALWTRP. This
includes similar weak link
requirements, as well as time-area
restrictions (e.g., Great South Channel).
NMFS believes the differences between
the hagfish and lobster trap/pot fishery
stated by the commenter would not
justify having the hagfish fishery being
treated differently.
Comment 261: One commenter
requested NMFS limit entry into the
shark gillnet fishery to vessels with
landing history using both sink gillnet
and driftnets. The commenter suggested
that NMFS should distinguish between
driftnets, strike nets, and small mesh
sink nets. In addition, the commenter
asked NMFS to define the relationship
of sink gillnets with anchors on ends
and shallow meshes to drifting deep
gillnets.
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Response: Limiting the number of
fishermen in a fishery, if resulting in
reduced fishing effort, may provide
conservation benefits to large whales.
However, such a management measure
is beyond the scope of this ALWTRP
final rule. NMFS may consider such
action in future rulemaking regarding
authorized gears and permit reform for
Highly Migratory Species (HMS)
fisheries. The current definitions in 50
CFR 229.2 explain the difference
between anchored (e.g., sink gillnet) and
driftnet gear.
Comment 262: Several shark
fishermen in the Southeast said they
lost 3 fishing days due to right whales
being in the area and fishermen moving
their gear. The commenter wanted this
to be acknowledged by NMFS.
Response: NMFS appreciates the
efforts of these fishermen and their
participation in helping to conserve
highly endangered right whales. See
response to Comment 274.
Comments on Enforcement
Comment 263: Several commenters
stress the need for strong enforcement
and believe there is no mechanism or
system (e.g., enforcement strategy) or
timeframe for handling violations or
monitoring compliance in the proposed
rule. One commenter states that the
existing regulations are under-enforced,
and that adequate enforcement of
existing regulations would protect
whales sufficiently.
Response: Enforcement of the
ALWTRP regulations is essential to their
success. Current regulations are being
enforced and increased enforcement
would likely lead to increased
compliance. The mechanism for
enforcement is through a partnership
between NMFS Office of Law
Enforcement (OLE), the USCG, and state
enforcement entities. Monitoring
compliance levels at sea is challenging
because of the complexity and
geographic expanse of the fishing
activity subject to the ALWRTP. NMFS’
strategy is to partner with state entities
as many states have personnel and
vessel resources available for marine
resources compliance monitoring. These
partnerships have yielded some
excellent results. For example, a short
duration random survey of lobster gear
was conducted by the Maine Marine
Patrol along the coast of Maine in 2004.
This 30 day survey demonstrated a 98percent compliance rate with ALWTRP
requirements.
Comment 264: Commenters stated
that NMFS needs some kind of
enforcement where either states or the
federal government is able to lift these
nets and make sure they are in
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compliance, because every time NMFS
writes a rule, the commenter believes
that the honest fishermen are being
punished.
Response: NMFS is aware of the
desire to haul gear to monitor
compliance with ALWTRP
requirements. Federal funds have been
made available to state enforcement
entities. Some of these funds have been
utilized to purchase or lease/rent vessels
capable of hauling trap/pot gear. Law
enforcement also can board a vessel and
observe as the operator retrieves gear to
monitor compliance with gear
requirements. NMFS seeks to identify
non-compliant fishermen in its
enforcement efforts.
Comment 265: One commenter
suggested developing an enforcement
plan that outlines agencies with
authority, the role of each agency with
authority, and a letter of agreement
among authorities for timely and
efficient enforcement.
Response: The authority and the role
of individual agencies with respect to
species covered by the ALWTRP is
determined directly by the ESA and the
MMPA. The USCG provides the
resources, personnel, and expertise for
enforcement at sea while NMFS
provides case development and
prosecution. Coastal states have
assumed an increased role in
enforcement at sea.
Comment 266: One commenter
requested that NMFS mandate new
reporting programs where fishermen
report in real-time where they are
placing fishing gear and where the gear
is being lost.
Response: NMFS is concerned about
lost gear and collects data on losses. For
example, in the Federal lobster fishery,
data are collected about losses that
exceed the allocated gear loss
allowance. The fishing gear types that
the ALWTRP regulates are
predominantly lobster trap and multi
species sink gillnet. Federal lobster and
gillnet fishery reporting requirements
collect some location information
through vessel trip reports. State lobster
fishery management plans monitor
effort by distinct fishing areas under an
interstate fishery management plan.
Neither of these processes is real time as
suggested by the commenter.
As of November 22, 2006, all limited
access Northeast multi-species vessels
(which would include sink gillnet
activities) are required to use real time
reporting of vessel location through the
vessel monitoring system (VMS). VMS
is being considered for the entire
groundfish fleet, which would include
sink gillnet activities, under Framework
42. VMS is also utilized in the shark
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gillnet fishery. Presently, there is no
VMS requirement for lobster trap/pot
gear.
The requirements to tag lobster traps
and some gillnet fishing activities
allows NMFS to identify individual
traps and some net panels by discreet
identification numbers.
Comment 267: One commenter
acknowledged and encouraged NMFS’
plans to convene an ALWTRT Subgroup
on monitoring.
Response: A Status Report Review
Subcommittee, which will address
monitoring, has been established as an
outcome of the April 2005 ALWTRT
Meeting.
Comment 268: One commenter stated
a perceived lack of enforcement in the
Gulf of Maine, which was brought up at
the last NEFMC meeting. The
commenter stated that the NEFMC was
briefed on NMFS’ enforcement efforts
and cooperation with the states.
Response: NMFS has increased
enforcement of ALWTRP regulations in
the Gulf of Maine, George’s Bank, and
Southern New England. This has been
done through USCG efforts and through
state-Federal partnerships over the past
3 years. The states of Maine,
Massachusetts, and Rhode Island have
received funds to conduct at sea
enforcement of ALWTRP regulations.
Comment 269: One commenter stated
that NMFS should address the fact that
the State of Maine has apparently not
mandated compliance with the
protocols used under the Atlantic Large
Whale Disentanglement Network.
Response: The State of Maine has
developed a conservation program that
assumes a larger role, relative to many
states along the eastern seaboard, in the
disentanglement of large whales. NMFS
has worked closely with the state on the
development and evolution of the
conservation plan and believes Maine is
operating in accordance with the
protocols.
Comment 270: One commenter
believed year-round requirements in the
EEZ would facilitate enforcement,
whereas a three month exemption in the
Mid-Atlantic (as in Alternative 3) would
be problematic for enforcement.
Response: The enforcement
community has experience with a large
number and variety of time-area
closures and gear restricted areas in the
Mid-Atlantic as well as the Northeast.
NMFS believes the 3-month period in
question, versus year round
requirements, may not be optimum in
terms of enforcement but has been
selected to reduce regulatory impacts on
the fishing industry during periods
when whales are infrequently sighted in
that area.
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Comment 271: One commenter said
that the Commonwealth of
Massachusetts will prosecute fishermen
if rope is found on a whale.
Response: The Commonwealth of
Massachusetts has a long history with
whales and disentanglement given the
unique characteristics of Cape Cod Bay
and Massachusetts state waters. The
primary focus of removing rope from
entangled whales is to reduce the
likelihood of serious injury or mortality.
The secondary focus of removing ropes
from whales is to learn more about how
whales become entangled. This
information may aid in the design of
gear which can reduce the likelihood of
future serious injury or mortality.
Fishermen are an important resource in
the study and development of gear
modifications. NMFS is not aware that
any fisherman has been prosecuted for
the entanglement of a whale by the
Commonwealth of Massachusetts.
Comment 272: Two commenters
stated that enforcement will be difficult
between commercial and recreational
fishermen and an exemption line may
increase resentment and noncompliance. One comment stated that it
will be hard to distinguish between
commercial and recreational gear at sea.
Response: The ALWTRP does not
regulate recreational fishermen. Some
states, such as the Commonwealth of
Massachusetts, have regulations for the
protection of right whales that apply to
some of the recreational and commercial
fisheries under their jurisdiction.
Massachusetts prohibits recreational
lobster traps in Cape Cod Bay during
certain times of the year and
differentiates commercial from
recreational gear through a gear marking
scheme. See response to Comment 237
for information on the management for
marine mammal interactions with
recreational fisheries.
Comment 273: One commenter
expressed concern with the difficulty of
enforcing weak link breaking strengths
and 30-day soak time limits.
Response: NMFS recognized the
difficulty in determining breaking
strengths of different types of weak links
when the plan was first developed.
Industry outreach has been conducted
demonstrating a variety of weak link
types and their associated breaking
strengths. Training on ALWTRP gear
requirements is provided to the USCG
Fisheries Training Centers and state
enforcement entities. Several
manufacturers have developed
commercially available weak links of
various breaking strengths which can be
purchased at fishing supply stores.
These weak links typically have the
breaking strength shown in raised letters
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on the actual weak links. NMFS also has
fishing industry outreach specialists.
These individuals have experience with
fishing gear and are available to evaluate
weak links for the fishing industry and
law enforcement agencies. Thirty-day
soak limits have been enforced.
Enforcement actions based on the 30day soak time limit were taken in 10
cases in 2005.
Comment 274: One commenter states
that there was an issue in the southeast
regulations with shark net gear that say
the gear has to be removed if right
whales, humpbacks, or finbacks are
located within 3 nautical miles (5.6 km).
However, it is not clear to the
commenter how that would be
accomplished or who would identify
the whales being within 3 nautical miles
(5.6 km) of the gear.
Response: NMFS, consistent with
recommendations from the ALWTRT,
believes fishermen are motivated to
avoid potential gear conflicts with
whales. However, other measures are in
place to aid fishermen in preventing
potential whale/gear interactions. In the
Southeast, an Early Warning System
(EWS) is maintained by the Southeast
U.S. Right Whale Recovery Plan
Implementation Team (SEIT) and its
partners. Near real-time data, including
the number of whales, location (latitude
and longitude) of whales, and direction
of their travel, are transmitted to
numerous interested stakeholders such
as shipping agents and commercial
mariners, including fishermen, via
pagers and email notifications.
Information is also received by
operation dispatchers, who then relay
the details to their vessels. General
locations for animals are also broadcast
over Marine VHF. NMFS believes that
these measures relay critical whale
information to fishermen, but will
continue to work with the SEIT and its
partners, as well as fishermen, to
facilitate and improve the distribution
of sightings information.
Comment 275: One commenter states
that VMS is not 100-percent reliable,
there are battery failures and
mechanical failures. This commenter
also believes that it costs a lot of money
for nothing and that some fishermen
have VMS that may not need them.
Response: NMFS believes VMS is
appropriate to substitute for 100-percent
observer coverage in the Southeast U.S.
Monitoring Area as defined in this final
rule. The system offers NMFS the ability
to monitor vessel timing and location
across management boundaries, enables
effective, coordinated dockside or at-sea
inspections, and facilitates coordination
with other enforcement agencies.
Although self-installation of VMS units
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has been permitted, subsequent
problems have been noted (e.g.,
insufficient power supply and improper
wiring). NMFS encourages fishermen to
have units installed by the
professionals. Power must be consistent
to allow each unit to report properly,
and NMFS suggests that fishermen
maintain a backup battery for this
reason. Once battery power has been
drained, the unit will not send reports
and significant damage to it may occur.
NMFS law enforcement and approved
vendors are improving unit models and
pursuing alternatives to detect battery
power and stop reporting/power usage
until the unit is fully powered again. If
units do malfunction, individuals
should coordinate with Southeast
Enforcement VMS personnel.
Otherwise, fishermen are encouraged to
have a vendor or electrician tend to the
unit; vessel operators are advised to not
leave port until the unit is repaired, in
accordance with regulations.
Comment 276: One commenter said
that several people in New Jersey and
other places would never run a shark
gillnet south of Jacksonville, but will be
required to use mandatory VMS and
was wondering if that was the intent of
the rule and asked whether NMFS was
considering the issue again and
considering a change.
Response: Although monitoring shark
fishermen off New Jersey and
surrounding areas was not the intent of
the VMS requirement, in the regulations
for Highly Migratory Species (HMS),
these data will allow NMFS to obtain a
better understanding of the shark fishery
in this area, including if fishermen
move farther south into the Southeast
U.S. Monitoring Area. See Comment
275.
Comment 277: Several commenters
said that although there are some
operational issues to consider regarding
VMS, some commenters preferred this
over the observer requirement in the
Southeast.
Response: NMFS agrees that VMS is
appropriate for the Southeast U.S.
Monitoring Area as defined in this final
rule, and will work with fishermen to
overcome operational issues. See
Comment 275.
Comment 278: Several commenters
stated that the Observer Program (i.e., a
fishery monitoring program where an
observer goes to sea with the fisherman)
and VMS (i.e., an electronic vessel
tracking system) are duplicative. These
commenters agreed that the VMS device
is expensive as well as difficult to
install, activate, and maintain. One
commenter suggested that, in light of
the problems associated with the VMS,
fishermen should not be liable if the
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VMS device does not indicate whether
it is functioning properly.
Response: NMFS disagrees that VMS
and observer coverage are duplicative,
as each program serves a different
purpose. The Observer Program is
intended and designed to collect
fisheries-dependent physical, biological,
and economic data, which can then be
used in stock assessments and also
verify logbooks; the program is not
meant for compliance monitoring. In
contrast, VMS’ primary purpose is the
monitoring and enforcement of timearea closure restrictions, as well as gear
compliance.
NMFS believes it is the responsibility
of fishermen to make sure that their
VMS units are functioning properly. If
units malfunction, individuals should
coordinate with Southeast Enforcement
VMS personnel or contact a vendor or
electrician to tend to the unit; vessel
operators are advised to not leave port
until the unit is functioning properly.
See Comment 275.
Comments on the Shipping Industry
and/or Ship Strikes
Comment 279: Numerous commenters
stated that NMFS needs to address the
shipping industry (e.g., tankers,
freighters, large ships, and ocean liners)
and the Navy, as ship strikes are the
leading cause of serious injury and
death to large whales (as opposed to just
regulating commercial fishermen). One
commenter requested that NMFS
address shipping and cruise industry
ship strikes before prohibiting floating
groundline.
Response: NMFS acknowledges and
appreciates the commercial fishing
industry’s involvement in the ALWTRT
and the modifications already made to
reduce the risk of serious injury and
mortality of large whales. NMFS agrees
that ship strikes and the need to
mitigate the risks posed by vessel traffic
is also important to large whale
conservation and recovery. As such,
NMFS is simultaneously pursuing other
rulemaking strategies and policy
discussions to address the threat of ship
strike. The Northeast and Southeast
Implementation Teams (NEIT/SEIT) for
the recovery of the North Atlantic right
whale include representatives from
various Federal agencies, such as the
Navy and the USCG, state agencies, port
authorities, and the shipping industry.
Based on information and
recommendations provided by these
groups, NMFS developed and published
a propose rule for right whale ship
strike reduction in the Federal Register
(71 FR 36299, June 26, 2006). The
proposed rule presents regulatory
measures that NMFS is considering to
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reduce the risk of ship strike to right
whales, such as speed restrictions and
vessel routing measures.
The proposed rule is one component
of a suite of comprehensive right whale
ship strike reduction measures, which
also includes education and outreach to
commercial and recreational mariners,
research on technologies that may help
mariners avoid whales, a
comprehensive program of sighting
advisories to mariners, section 7
consultations to address Federal vessel
activities, and the development of a
Conservation Agreement with Canada.
As Federal agencies, under section 7
of the ESA, the branches of the U.S.
military are required to consult with
NMFS (or U.S. Fish and Wildlife
Service) to ensure that their actions are
not likely to jeopardize the continued
existence of any endangered or
threatened species or result in the
destruction or adverse modification of
critical habitat. Both the U.S. Navy and
the USCG have undergone ESA section
7 consultations on various activities that
may affect large whales. In addition, the
U.S. Navy and USCG implement
internal policies regarding marine
mammals, including marine mammal
observer training, restrictions on
activities in protected areas and
important habitats, reporting of any
dead or injured whales sighted and
mandatory reporting of any interactions
with marine species.
NMFS recognizes both entanglement
and ship strike as human-caused
sources of serious injury and mortality
to large whales that need to be
addressed in order to recover these
species. Floating groundline has been
identified as an entanglement risk to
whales, and is therefore being addressed
in this final action.
Comment 280: Many commenters said
that more should be done to reduce the
mortality of whales due to commercial
and military ship strikes. Commenters
stated that NMFS has not found a
solution to ship strikes or entanglements
and little has been done. Other
commenters believed that, though
commercial and naval ships pose the
greatest threat to whales’ existence,
these ships continue to operate largely
unregulated. Several commenters
believed that ship strikes occur more
often than previously thought.
Response: NMFS agrees that ship
strikes are a source of mortality to large
whales that needs to be addressed in
order to recover these species. See
response to Comment 279. NMFS
acknowledges that historic reports of
ship strikes may not accurately
represent the frequency of ship strikes
due to the lack of a central reporting
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mechanism. Although current reporting
practices and improved knowledge
about the types of wounds inflicted by
ship strikes have improved
understanding of ship strikes, many
ship strikes are still likely to go
undetected or unreported.
Comment 281: One commenter states
that more whales are hurt by ships
outside three miles (5.6 km) than by
rope and buoys used in fishing
operations.
Response: Because many ship strike
and entanglement events are
unobserved at the time the incident
actually occurred, it is difficult to
determine where whales are struck or
become entangled. In addition, many
entanglement and ship strike events
likely go undetected. As such, it is
difficult to draw conclusions about
where these events occur and whether
ship strike or entanglement poses a
greater threat to large whale
populations. NMFS recognizes both
entanglement and ship strikes as
human-caused sources of serious injury
and mortality to large whales that need
to be addressed in order to recover these
species, and is undertaking regulatory
efforts to address both issues. See
response to Comment 279.
Comment 282: Two commenters
stated that the LNG Terminal, which is
located in the summer feeding ground,
will result in vessels going through the
feeding grounds, which is more
dangerous than entanglement risk. One
of these commenters believes that it is
wrong to put a proposed LNG terminal
into the Critical Habitat Area. The
commenter states that the big propellers
on the patrol boats are more apt to kill
a whale then some fishing gear.
Response: While NMFS appreciates
the concern raised, the current action
addresses the effects of entanglement in
commercial fishing gear on large
whales. The effects of other marine
resource uses, such as commercial
shipping and offshore LNG terminals,
are being addressed through other
regulatory and management processes.
LNG terminals are licensed by other
Federal agencies, which are subject to
the requirements of section 7
consultation under the ESA. See
response to Comment 279.
Comment 283: Another commenter
mentioned that whales are beyond
Schoodic Ridge, west of Blue Nose
Buoy, and in deep water. The
commenter has seen large vessels
including a high speed ferry traveling at
50 knots (92.6 km) through feeding
whales. The commenter believes that
there should be regulations on ships,
and does not understand why
lobstermen are singled out.
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Response: NMFS agrees that ship
strikes and the need to mitigate risks
posed by large, fast-moving vessels are
important to large whale conservation
and recovery. As such, NMFS is
pursuing other rulemaking strategies
and policy discussions to address the
issue of ship strikes. See response to
Comment 279.
Comment 284: Some commenters
stated that NMFS should address all
sources of endangered whale mortality.
Many commenters were concerned
about the level of regulation on the
fishing industry relative to other causes
of mortality like shipping and land
based activities (e.g., water quality
issues). One commenter pointed to
those which endanger whales by
disposing of waste at sea as another
example of an unregulated group that is
not reached by today’s regulations.
Some commenters stated that all
industries should share the regulatory
burden, yet some are unregulated (e.g.,
shipping and Canadian fishing gear).
Other commenters stated that NMFS
should seek a comprehensive whale
protection strategy that takes other
impacts into account nationally and
internationally to share the
responsibility of conservation efforts.
Response: NMFS realizes that other
marine resource user groups are
affecting large whale populations, and
NMFS will continue efforts to reduce
these impacts. NMFS is pursuing
various regulatory and non-regulatory
strategies for reducing the impact of
vessel collisions on northern right
whales. See response to Comment 279.
Many ocean disposal and discharge
activities require permits issued by
other Federal agencies such as the U.S.
Environmental Protection Agency and
the U.S. Army Corps of Engineers.
Under section 7 of the ESA, any Federal
agency issuing such a permit must
consult with NMFS (or U.S. Fish and
Wildlife Service) to ensure that the
issuance of the permit is not likely to
jeopardize the continued existence of
any endangered or threatened species or
result in the destruction or adverse
modification of critical habitat. Section
7 consultations often result in
restrictions and mitigation measures
that are required of the permit applicant
in order to reduce impacts to
endangered species.
NMFS also continues to participate in
international fora that address impacts
to large whales. NMFS is continuing to
work with Canadian biologists and to
support efforts to expand
disentanglement efforts in Canadian
waters. NMFS will continue to work
with the government of Canada toward
development of similar protective
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measures from fishing operations for
right whales in Canadian waters. NMFS
has also initiated discussions regarding
an International Conservation
Agreement for right whales with
Canada, which would include the
impacts of shipping on right whales.
The Conservation Committee of the
International Whaling Commission
(IWC) identified ship strike as a priority
item in the conservation agenda, and
recently formed a ship strikes working
group to assess the level of threat caused
by maritime traffic worldwide and to
examine policies that could be
implemented to mitigate the impact of
ship strikes. The International Maritime
Organization (IMO) has reviewed and
approved proposals to address the
impacts of shipping on marine
mammals, including approval of the
right whale Mandatory Ship Reporting
System in 1998 and the shifting of the
Bay of Fundy shipping lanes in Canada
in 2003. In December 2006, the IMO
approved a proposal to shift the Boston
Traffic Separation Scheme to reduce the
overlap between heavy shipping traffic
and large whales.
International organizations such as
the IWC and the International Council
on the Exploration of the Sea (ICES) are
examining the effects of ocean noise on
marine mammals, including the noise
generated by shipping, oil drilling, and
seismic exploration. NMFS convened
the first international symposium on
shipping noise and marine mammals in
2003. All of these groups are
considering strategies for managing
human-produced noise sources in the
marine environment.
Many of NMFS’ activities to promote
the conservation and recovery of large
whales are directed by actions outlined
in recovery plans developed in
accordance with the ESA. Recovery
plans are designed to provide
comprehensive strategies for recovering
endangered species.
Comment 285: Several commenters
believe that the negative impacts of the
whale watch industry need to be
assessed. One commenter said that there
is a problem with whale watching
vessels getting too close to whales.
Response: NMFS monitors the
activities of the whale watch industry.
NMFS has developed a set of whale
watching guidelines for the Northeast,
which outline appropriate speed limits
and approach distances to reduce the
potential for harassment of whales.
NMFS also has a regulation prohibiting
approaching closer than 500 yards (1500
ft, 457.2 m) to a right whale. NMFS
conducts active outreach to whale
watch companies to encourage
compliance with these guidelines.
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NMFS is also working on a proposed
rule to minimize the potential for future
serious injury and mortality of whales
from whale watch vessels.
Comment 286: One commenter asked
why NMFS is not attacking the real
problem, which the commenter said is
cruise ships, ferries, tankers, and whale
watchers. The commenter said some
vessels leave Bar Harbor going 35 miles
an hour (56.3 km/h), and he hears on
the radio about the whales they are
seeing. The commenter said that these
vessels could be chasing whales into
fishing gear.
Response: NMFS is currently
pursuing a comprehensive strategy of
regulatory and non-regulatory measures
to reduce the impact of shipping on
right whales. See response to Comment
279. Although it is possible that a whale
could become entangled in fishing gear
while attempting to escape an oncoming
vessel, NMFS is not aware of such an
event being documented. Researchers
continue to investigate the
circumstances under which whale/gear
and whale/vessel interactions occur.
Comments on Gear Reduction
Comment 287: Two commenters
referenced LMA 3 as an area where
there was a reduction in lobster traps
being fished. One commenter urged
NMFS to consider the recent LMA 3
offshore historical qualification process
that reduced the number of offshore
permits from 968 to 133 and the number
of traps from approximately 400,000 to
160,000. The other commenter stated
that in LMA 3 there has been a 40percent reduction in traps fished. The
commenter stated that trap reduction is
the most valuable way to stop
interaction with whales. Another
commenter stated that reducing the
number of traps in an area, such as in
LMA 3 will be better than gear
modifications and it will better help
protect whales. The Federal lobster
management plan identifies and
restricts the number of fishermen able to
fish offshore, and this smaller number of
fishermen will reduce their traps,
buoylines, and loops. The commenter
estimated a nearly 50 percent reduction
over the next five to seven years. One
commenter states that the overall
amount of gear and fishing effort will be
reduced over the next couple of years.
The commenter states the number of
lobstermen is declining from 3,000 to
less than 150 and the amount of gear in
the water will decline by more than 40
percent.
Response: NMFS acknowledges the
effort reductions that are occurring in
LMA 3, and agrees that this should help
reduce serious injury and mortality of
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large whales. NMFS believes these effort
reductions will be critical to future
discussions with the ALWTRT on how
to reduce risk associated with vertical
line. However, NMFS believes reducing
risk associated with groundline through
this final rule is appropriate even with
the effort reductions occurring offshore.
Additionally, with this final rule, NMFS
intends to address all fishing gear that
poses a risk to large whales similarly.
Comment 288: One commenter states
that the figures in the DEIS do not
reflect an additional two-year lobster
gear reduction along with continual
passive reductions through a proposed
trap transferability plan recommended
to the ASMFC. The commenter would
like to see a trap buyback to further
reduce the number of traps to help
whales and the lobster fishery.
Response: The commenter is likely
referring to Addenda IV and V to the
Lobster FMP. As discussed in Chapter 9
of the FEIS, Addendum IV as initially
proposed incorporated an accelerated
trap reduction program and the
implementation of a transferable trap
program in LMA 3 (among other
provisions). ASMFC deferred action on
this proposal, opting instead to address
this issue under Addendum V. The
approach originally outlined in
Addendum IV proposed an overall trap
cap of 2,600 traps and a two-tiered tax
on the purchase of traps, with a higher
tax applied when the purchaser owns
2,100 traps or more. In response to
concerns raised at public hearings that
a 2,600 trap cap may be too high, the
LMA 3 Lobster Conservation
Management Team (LCMT) amended its
original proposal under Draft
Addendum V. Addendum V proposed a
cap of 2,200 traps and a two-tiered tax
on the purchase of traps, with a higher
tax imposed when the purchaser owns
1,800 or more. Addendum V was
approved by the Board at the March
2004 Board meeting and went into effect
in 2005.
NMFS and others have supported
buybacks of groundline. See response to
Comment 93. Limiting the number of
traps in a fishery, if resulting in reduced
fishing effort, may provide conservation
benefits to large whales. However, this
management measure is beyond the
scope of this final rule. NMFS is
pursuing measures such as trap effort
reduction through other rulemaking
actions (e.g., 70 FR 24495, May 10,
2005).
Comments Regarding Canadian Gear/
Fisheries
Comment 289: Several commenters
said that Maine fishermen mark
balloons with fishermen’s name, harbor
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name, and boat name. Commenters
stated that most balloons picked up that
are not marked come from Canada.
Another commenter said that he fears
being evicted from the lobster grey area
because Canadian and U.S. gear is being
fished side by side and one would not
be able to tell whose gear is responsible
for potential entanglements.
Response: NMFS disagrees with the
commenters’ claim that most recovered
polyballs or ‘‘balloons’’ that are not
marked come from Canada. Further,
NMFS notes that it is not revising the
ALWTRP based on the recovery of
unmarked polyballs or gear that may
have originated from the grey area. The
need for the revisions of the ALWTRP
is the continuing risk of serious injury
and mortality of Atlantic large whales
due to entanglement in commercial
fishing gear. NMFS considered several
factors when evaluating the
entanglement information: (1) A
mortality or injury may involve multiple
factors (e.g., whales that have been both
struck by a ship and entangled are not
uncommon); (2) the actual gear type/
source is often uncertain; and (3) several
types of gear may be involved in a given
reported entanglement. NMFS limits a
‘‘serious injury’’ designation to only
those reports that offer substantiated
evidence that the injury is likely to lead
to the whale’s death. Injuries that
impede the whale’s locomotion or
feeding are not considered serious
injuries unless they are likely to be fatal
in the foreseeable future.
Comment 290: One commenter
expressed concern over the lack of
Canadian take reduction efforts and gear
modification requirements. The
commenter expressed concern that all
entangled whales get counted against
U.S. fishermen.
Response: NMFS is issuing this final
rule specifically to address commercial
fishery impacts from U.S. fisheries.
NMFS acknowledges that entanglements
with fishing gear from Canadian
fisheries may also cause serious injury
and mortality to large whales. NMFS is
currently addressing these threats
through formal discussions with
Canada. For example, NMFS is working
with representatives from the Canadian
DFO to develop and implement
protective measures for right whales in
Canadian waters. The ALWTRP is
designed to respond to the threats posed
by domestic fishing gear.
Comment 291: Several commenters
state that NMFS should work more
closely with the Canadian Government
to harmonize American and Canadian
fishery regulations. They state that
Canadian fishing gear is a major cause
of whale entanglements that lead to
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injuries and mortalities. Commenters
encouraged NMFS to pursue parallel
conservation measures with the
shipping industry and military vessels
in the U.S. as well as Canada. One
commenter encouraged NMFS to work
with the Canadian Government through
the Canadian Species at Risk Act for
joint efforts to protect right whales.
Response: Coordination between
Canada and the U.S. concerning
transboundary marine mammal and
other protected species has been
ongoing since mid-1990. In earlier years
the coordinated efforts focused on
broader issues concerning Atlantic
salmon, harbor porpoise, and right
whales. At that time, most of the issues
regarding right whales were secondary
as both countries addressed other
pressing issues. Although both countries
continued to work cooperatively on
right whale issues, limited resources
prevented both countries from meeting
on a regular basis. However, in
anticipation of the implementation of
SARA, the group was reconstituted in
January 2003. The focus of the group
was still based on species-specific
conservation, but the charge for the
working group was expanded to include
joint assessments, listing criteria, and
recovery planning and implementation
in a broader sense to include all
transboundary marine mammal and
protected species stocks (with the
exception of Atlantic salmon). The
working group’s primary efforts are
toward right whale recovery efforts.
NMFS is continuing to work with the
Canadian Government to develop and
implement protective measures for right
whales in Canadian waters. In addition,
NMFS is working with Canadian whale
biologists and support teams to improve
and expand disentanglement efforts in
Canadian waters.
Comments on the Number of Traps per
Trawl
Comment 292: One commenter
encourages more traps per buoy line
whenever possible. For areas in eastern
Maine where sinking groundline cannot
be used, the commenter thinks reducing
line by shifting to longer trawls where
possible would be a viable option. The
commenter recommends a limit on the
number of traps per lobster trawls as an
emergency action. Another commenter
opposes putting limits on the number of
traps per trawl. The commenter states
that he cannot fish more than 25 traps
per trawl due to boat size.
Response: In this final rule, NMFS is
maintaining the status quo for the
minimum number of traps/pots with a
single buoy line in specific management
areas. Additionally, NMFS believes that
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reducing profile of groundline along the
east coast, including eastern Maine,
through this action is important to
reduce the serious injury and mortality
of large whale due to incidental
entanglement in commercial fisheries.
Options such as this for reducing risk
associated with vertical lines will be
discussed with the ALWTRT at the next
meeting.
Comment 293: One commenter
understands that NMFS is not proposing
to move nearshore requirements into
inshore waters. The commenter states
that there should not be restrictions
such as ‘‘no single traps’’ or ‘‘one buoy
line for less than five trawls’’ in inshore
waters. The commenter does not agree
with nearshore regulations being
expanded into inshore waters.
Response: As the commenter stated,
NMFS is managing inshore and
nearshore trap/pot waters differently
under the plan. NMFS will be
discussing options for addressing risk
associated with vertical line with the
ALWTRT at the next meeting, and will
pass along the commenter’s concerns.
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Comments on Vessel Anchoring
Systems
Comment 294: Many commenters
requested that NMFS investigate the
degree to which vessel anchoring
systems pose a risk to whales. For
example, according to the commenter,
in 2003, a humpback whale in
Stellwagen Bank National Marine
Sanctuary was entangled in a small boat
anchoring system. Additionally,
commenters stated that two humpback
whales were disentangled from
anchors—one gillnet and one vessel
anchoring system. These commenters
stated that NMFS does not consider
anchoring systems as a risk.
Response: Anchoring systems have
been recognized by NMFS as a risk to
large whales and have been addressed
by requiring sinking line on lines
leading from gillnets to the anchor. The
anchoring systems of small recreational
vessels in pursuit of fin fish in areas like
Stellwagen Bank National Marine
Sanctuary are not captured in the
ALWTRP process. See response to
Comment 237 for information on the
management of marine mammal
interactions with recreational fisheries.
Comment 295: One commenter states
that NMFS should require all vessel
anchoring systems to be brought back to
the dock and not left unattended.
Response: NMFS is considering future
rulemaking to address vertical line and
will be discussing these issues with the
ALWTRT at the next meeting. NMFS
will discuss the practice of vessel
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anchoring at sea with the ALWTRT at
that time.
Comments on Research
Comment 296: One commenter states
that research concerning right whale
behavior and its use of the water
column is needed as there are gaps in
information and high priority needs.
Response: NMFS agrees that more
research is needed on right whale
behavior and their use of the water
column. To try to gather this needed
information, NMFS developed a number
of right whale biological needs priorities
in support of the ALWTRP and included
these in the 2006 NMFS Northeast
Region’s Request for Proposals for right
whale research and Atlantic coast states
right whale recovery plan programs.
These priorities included the need for
research on the horizontal and vertical
distribution of right whales in the water
column, including over rocky bottom
and coral or wreck habitats, as well as
research on the temporal and spatial
distribution of right whales. In this final
rule, NMFS is implementing broadbased measures to further reduce the
risk of serious injury and mortality to
large whales from interactions with
commercial fishing gear. In the future,
NMFS will discuss with the ALWTRT
the results of any projects that study
right whale behavior and their use of the
water column.
Comment 297: One commenter urged
NMFS to consider right whale foraging
research, specifically the
recommendations from the Northern
Gulf of Maine Foraging Workshop. The
commenter stated a need to understand
if large whales forage in rocky and tidal
areas before requiring the investment in
new gear.
Response: NMFS agrees that more
information must be collected on large
whale foraging behavior in rocky and
tidal areas and some of this information
is currently being gathered. For
example, Maine DMR is working with a
number of whale research organizations
to gather zooplankton data along the
coast of Maine to help determine if right
whales may be foraging there. Once
these data are collected and analyzed,
the resulting information will be
presented to the ALWTRT. At the
present time, for both right and
humpback whales, serious injuries and
mortalities resulting from interactions
with commercial fishing gear regulated
under the ALWTRP continue to occur,
and PBR has been exceeded. PBR for the
North Atlantic stock of right whales is
set at zero and for the Gulf of Maine
stock of humpback whales, PBR is set at
1.3 (Waring et al., 2006). Therefore,
NMFS is required to take additional
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action to further reduce serious injury
and mortality to large whales resulting
from interactions with commercial
fishing gear regulated under the
ALWTRP. Also, see response to
Comment 296.
Comment 298: One commenter
suggested NMFS conduct research
concerning large whale prey
distribution and whale foraging areas,
and how these tie into effective gear
marking and how to effectively reduce
risk of vertical lines.
Response: This is an area that both
NMFS and the ALWTRT recognize as
important. A variety of organizations are
already conducting research on large
whale prey items; for example, Maine
DMR is working in conjunction with a
number of whale research organizations
to gather zooplankton data in Maine
waters. In addition, NMFS developed a
number of right whale biological
priorities in support of the ALWTRP
and included these in the 2006 NMFS
Northeast Region’s Request for
Proposals for right whale research and
Atlantic coast states right whale
recovery plan programs. One priority
included the need for research on the
vertical distributions of both the
processes and the prey organisms
related to right whale foraging for
habitat characterization and predictive
modeling. See response to Comment
307.
Comment 299: Several commenters
suggested NMFS research humpback
and finback whale foraging, given they
feed on different prey items than right
whales. One commenter said that more
whale research is needed to identify
foraging areas, the availability of food,
how it affects whales, migration
patterns, and feeding habitats.
Response: NMFS agrees and
continues to conduct research, as well
as support research conducted by NMFS
partners, on all the above mentioned
topics.
Comment 300: One commenter
suggested that NMFS work with Maine
DMR to periodically review whale
foraging and distribution and other
sources of mortality.
Response: NMFS agrees and will
continue to work with Maine DMR and
other entities, including the ALWTRT,
to study and review factors affecting
whale foraging, distribution, and other
sources of mortality.
Comment 301: One commenter
suggested using humpback whales as
proxies for right whales when testing
new technology because of the larger
population (i.e., permitting may be
easier).
Response: As indicated in the FEIS for
the SAM interim final rule (67 FR 1142,
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January 9, 2002) and this final rule, it is
not feasible to conduct and evaluate
experiments on right or humpback
whale interactions with modified gear
configurations. For obvious reasons,
NMFS cannot conduct field tests or
laboratory experiments on right or
humpback whales to collect data to test
new gear technology. However, NMFS is
able to analyze past entanglement
events and develop ways to modify gear
in order to reduce risk of serious injury
and mortality from future entanglement
events. This information is discussed in
the forum of the ALWTRT. In terms of
gathering biological information on right
whales, NMFS believes that in some
cases humpback whales may be used as
proxies for right whales. However, in
most instances, right and humpback
whales differ ecologically and
behaviorally, so data collected on
humpback whales may not be
transferred to right whales in all cases.
For example, humpback whales could
not be used as a proxy to examine the
entanglement risks associated with
foraging behavior of right whales
because the two species differ in their
prey items as well as in the techniques
they use to capture their prey.
Comment 302: Two commenters
requested that NMFS consider the
relative role of gear entanglements when
compared to overall mortality estimates.
Response: Currently, there is no
reliable method for estimating the
number of large whales that die each
year from entanglements, although
recovered carcasses do provide
minimum values. However, NMFS is
responsible for applying the mandates
and requirements set forth in the ESA
and MMPA. Section 118 of the MMPA
requires that NMFS reduce incidental
mortality and serious injury of marine
mammals resulting from interactions
with commercial fishing gear. For this
reason, it is not necessary to compare
the relative role of fishing gear
entanglements with overall large whale
mortality estimates because by law,
NMFS is required to address the issue
of large whale interactions with
commercial fishing gear. The FEIS
provides a complete description of the
status of the large whale stocks that are
covered under the ALWTRP as well as
the effects of commercial fishing on
these species. Further, the PBR rate for
North Atlantic right whales, as
described in Waring et al., 2006, is zero.
The PBR for the Gulf of Maine stock of
humpback whales is 1.3. For both right
and humpback whales, serious injuries
and mortalities resulting from
interactions with commercial fishing
gear regulated under the ALWTRP have
occurred, and PBR has been exceeded.
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Therefore, NMFS is required to take
additional action to further reduce
serious injury and mortality to large
whales resulting from interactions with
commercial fishing gear regulated under
the ALWTRP. NMFS is implementing
this final rule to further address large
whale entanglements in commercial
trap/pot and gillnet fisheries along the
U.S. east coast. NMFS appreciates the
work of all trap/pot and gillnet fishing
industry members that are involved in
the ALWTRT process.
Comment 303: One commenter stated
that little gear testing has been done in
the Southeast.
Response: A variety of gear research
and testing, in particular focusing on
gillnet gear, has been conducted by
NMFS from North Carolina through
Florida in conjunction with commercial
fishermen. For example, for the sink and
shark gillnet fisheries, NMFS has
collected load cell data on the strains
exerted when hauling the gear, as well
as load cell data on the loads exerted on
buoy and anchoring systems. These data
are useful in making determinations
about the operational feasibility of
different weak link breaking strengths in
these fisheries. In addition, NMFS is
continuing to work with black sea bass
fishermen to assess the use of sinking
and/or neutrally buoyant groundline in
this fishery.
Comment 304: One commenter
requested that NMFS develop and
propose an evaluation method to
identify those gear modifications that
genuinely reduce risk and those that do
not make a difference in occurrence
and/or seriousness of large whale
entanglements. The commenter believes
this information is critical to assessing
and revising, as needed, gear
modifications under the ALWTRP.
Response: NMFS agrees that ALWTRP
management measures should be
evaluated. At the 2005 ALWTRT
meeting, a ‘‘Process for Considering
Gear Modifications under the ALWTRP’’
was finalized and approved by the
ALWTRT. This is a formalized process
that describes how NMFS and the
ALWTRT would handle gear
modification proposals. This process
identifies a standard set of questions
that would be used for evaluating and
responding to gear modifications. The
five categories used to evaluate gear
modification proposals are: product
description, feasibility, risk reduction,
relationship with current requirements
under the ALWTRP, and
recommendation of the ALWTRT. Gear
modification proposals or ideas would
be evaluated by regional ALWTRT
subgroups, and gear modification
recommendations from these subgroups
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would be presented to the full ALWTRT
for possible incorporation into the
ALWTRP.
Comment 305: One commenter
stressed the importance of gear research.
Additionally, commenters encouraged
NMFS to continue promoting research
initiatives that explore fishing
techniques that reduce entanglement
risk and develop new whale safe gear
(including low profile groundline).
Response: NMFS agrees that gear
research is an important component of
the ALWTRP. NMFS developed a
number of fishing gear research
priorities and included these in the
2006 NMFS Northeast Region’s Request
for Proposals for right whale research
and Atlantic coast states right whale
recovery plan programs. Such priorities
include the need for reducing the risk
associated with vertical line, as well as
research for reducing the profile of
groundline. The Right Whale Research
Program specifically solicits the
submission of idea projects in which a
new device or process is developed, as
well as pilot projects which involve
developing an idea or concept and
conducting at-sea testing involving one
or more members of the fishing
industry. The Atlantic Coast States
Cooperative Planning for Right Whale
Recovery Program encourages state
agencies to apply for funding to further
develop their right whale recovery
programs, which in many cases includes
conducting gear research. NMFS will
continue promoting these research
initiatives as funding allows and will
work through the ALWTRT to maintain
an updated list of gear research
priorities, as well as priorities related to
right whale biological needs in support
of the ALWTRP. NMFS encourages the
fishing industry, state partners, and
others to work collaboratively with the
agency to continue to develop new ideas
and techniques that will reduce
entanglement risk.
Comment 306: One commenter urged
NMFS to work with scientists on
devising an assessment program for
determining how effective individual
measures are for all whale species and
understanding fishing practices and
geography to adapt the plan
accordingly.
Response: NMFS agrees that the
ALWTRP management measures should
be evaluated and that this should be
done at the ALWTRT level, for which
scientists are members. At the 2004
ALWTRT meeting, NMFS formed a
Status Report Subcommittee that is
responsible for discussing various issues
including how the ALWTRT and NMFS
should evaluate the ALWTRP. Feedback
from the Status Report Subcommittee
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will then be provided to the full
ALWTRT. See also response to
Comment 305. The ALWTRT is
composed of a wide variety of
participants from many different
backgrounds, including state and federal
managers, scientists, the fishing
industry, environmentalists, fishery
management organizations, and more.
At each meeting, the ALWTRT is briefed
with the most recent available
information on a variety of topics,
including the species managed by the
ALWTRP, as well as information about
the fisheries that are regulated under the
ALWTRP. The Status Report
Subcommittee is the avenue by which
ALWTRP monitoring will be discussed.
Comment 307: One commenter
suggested combining the results of
whale-related and gear-related research.
The commenter encouraged further
research on the seasonal distribution of
buoy lines and the number of traps
fished per buoy as well as the seasonal
distribution of whale sightings and their
prey (i.e., look at the probability of how
these overlap in real time).
Response: This is an area that both
NMFS and the ALWTRT are interested
in exploring. NMFS is presently
supporting an analysis that is examining
the seasonal and temporal distribution
of vertical lines for all trap/pot and
gillnet fisheries. In addition, much right
whale research is being conducted and
supported by NMFS at this time. NMFS’
NEFSC is currently conducting research
to ultimately compare the density of
fishing gear to the density of whales to
develop a better picture of potential
overlap. Ecological work is also being
carried out in the Great South Channel
to see how right whales are interacting
with the sea floor; results will help
NMFS gain a better understanding of
whale interactions with fixed fishing
gear. Right whale foraging research is
also being conducted and forms the
foundation of critical habitat analyses
currently being preformed by NMFS.
Once these analyses are finalized, the
results will be compiled and distributed
to the ALWTRT. These results will then
be used by NMFS and the ALWTRT
when discussing different management
options that can be used to reduce
entanglement risk associated with
vertical lines.
Comment 308: Commenters urged
NMFS to do more research on: (1)
Fishing gear that works reliably and
safely, under all weather conditions;
and (2) how whales interact with fishing
gear in order to know what kind of gear
will keep whales free of entanglement.
Response: NMFS is committed to gear
research and development and will
continue to develop reliable and safe
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gear modifications. NMFS has gear
laboratories and research teams that
specifically focus on gear development
and testing, incorporating tides, sea
conditions, weather conditions, load
cell data, and the size/and or weight of
gear into their analyses. Additionally,
NMFS contracts with researchers,
individuals and companies to develop
gear solutions.
NMFS agrees that it would be useful
to determine how whales directly
interact with fishing gear. However this
would be difficult research to conduct
without endangering right whales
further, and is thus, not particularly
tractable at this time.
Comment 309: One commenter stated
that there needs to be more research
done to examine appropriate gear
modifications when necessary.
Response: See response to Comment
306.
Comment 310: One commenter
suggested that NMFS research include
exempted areas.
Response: NMFS is working with
states to help monitor exempted areas.
Based on analysis of sightings data,
NMFS understands that large whales
may occasionally be reported in
exempted waters such as bays and
harbors, but believes that these
occurrences are rare. If, in the future,
whales are more frequently reported in
exempted waters, NMFS and the
ALWTRT will reevaluate the exemption
lines for those particular areas to
determine whether changes are needed.
Comment 311: One commenter
requested that NMFS develop a
prioritization scheme for granting
scientific research permits that address
critical bycatch, entanglement, or other
conservation needs.
Response: NMFS recognizes the
concern, however, it is not within the
scope of this final rule.
Comment 312: One commenter
questioned a NMFS study that indicated
that more than 90 whales were killed
between the early 1990s and 2002. The
commenter asked what the cause of
death was in each case and specifically
whether any were linked to lobster
fishing because the study mentions ship
strikes as cause of death. The
commenter also requested a breakdown
by year to determine whether there is an
upward or downward trend during the
reporting period. The commenter stated
that data from 2003–04 are not
presented, so it is difficult to determine
if current steps taken by fishermen are
working since not enough time has
elapsed.
Response: For updated and complete
reports on large whale mortality
estimates, NMFS suggests Waring et al.,
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(2006) and/or Cole et al., (2006). Data
the commenter cites may not have been
available when the DEIS was originally
formulated; the report would have since
been incorporated into current analyses
where feasible. See Comment 4.
Comment 313: One commenter stated
that the DEIS does not address the
remotely operated vehicle (ROV)
research conducted in Maine.
Response: NMFS has added text to
Chapter 5 in the FEIS to address this
research.
Comment 314: One commenter asked
if NMFS is assuming that entanglement
risks occur solely during foraging since
research on other cetacean behavior and
entanglement risks is not suggested.
Response: While the nature of
foraging behavior is consistent with the
mouth entanglements recorded, NMFS
does not assume this is the only
cetacean behavior that leads to
entanglements. The potential for
entanglement as a result of different
behaviors is suggested by both the
diverse geographic locations in which
entanglements occur (see Chapter 4 of
the EIS) and the parts of the whale on
which gear or scarring are found (see
Chapter 2 of the EIS).
Comments on Economic and Social
Impacts (of the ALWTRP)
Comment 315: Several commenters
suggested that the government issue
grants to fishermen to help defray costs
and replace old gear.
Response: NMFS understands that
there are costs associated with
converting gear to become compliant
with the new ALWTRP requirements.
To date, NMFS has supported two
floating groundline gear exchange
programs, and their purpose was to
provide financial aid to commercial
fishermen to replace their floating
groundline with sinking and/or
neutrally buoyant groundline. The first
took place in 2004 and early 2005 and
included participation from
Massachusetts-licensed inshore lobster
trap/pot fishermen. The second took
place in January 2006 and sought the
participation of state and/or federally
licensed commercial trap/pot fishermen
in New Jersey, Delaware, Maryland,
Virginia, and North Carolina.
Approximately $200,000 was spent
replacing floating groundline with
sinking and/or neutrally buoyant
groundline in the Mid-Atlantic. Both
programs involved the collection of
actively fished floating groundline and
the issuance of vouchers that fishermen
used toward the purchase of sinking
and/or neutrally buoyant groundline. A
similar floating groundline exchange
program is underway for state and
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Federally licensed commercial trap/pot
fishermen in the State of Maine. For
additional information, see responses to
Comments 85 and 93.
Comment 316: One commenter asked
if it is possible for environmental groups
to contribute money to do more research
on whales and see where they go.
Response: NMFS welcomes
collaborative partnerships with any
group to help fund research on large
whale distribution.
Comment 317: One commenter
believes financial resources should be
allocated to research and development
and monitoring priorities as established
within the TRT working group process.
Response: NMFS agrees that gear
research is an important component of
the ALWTRP and that ALWTRP
priorities should be monitored. See
responses to Comments 305 and 306.
Comment 318: One commenter said
that the fishermen need resources
allocated in order to conduct a
collaborative research program that will:
(1) Document conditions in which
fishermen work; (2) allow fishermen to
work safely with no additional
economic burden; and (3) find common
sense answers and those applicable to
areas where people fish with hybrid or
other type of rope or gear that can be
used.
Response: NMFS welcomes fishermen
to apply for funding under the Right
Whale Research Program, which
requests proposals annually, contingent
upon available funding, and focuses on
funding projects that seek to reduce the
risk of serious injury and mortality to
right whales due to entanglement in
commercial fishing gear. NMFS
encourages the submission of proposals
seeking to develop new gear
modifications or pilot project designs to
test newly developed or even existing
gear modifications that have not yet
been field tested on a larger scale.
NMFS encourages applicants to work
closely with NMFS in the development
of ideas or concepts. Ideas or concepts
that have been developed through this
program, or through other means, will
be presented/provided to the ALWTRT
for discussion.
Comment 319: Some commenters
stated that right whales are a federally
protected species and, therefore, should
be free of all entanglement and mortality
risks due to fishing gear, regardless of
the potential economic consequences
for the fishing industry.
Response: NMFS is responsible for
applying the mandates and
requirements set forth in the ESA and
MMPA. Accordingly, section 118 of the
MMPA requires that NMFS reduce
incidental mortality and serious injury
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of marine mammals resulting from
interactions with commercial fishing
gear. The FEIS provides a complete
description of the status of the large
whale stocks that are covered under the
ALWTRP as well as the effects of
commercial fishing on these species.
Further, the PBR rate for North Atlantic
right whales, as described in the most
recent U.S. SAR, is set at zero.
Similarly, the PBR rate for the Gulf of
Maine stock of humpback whales is set
at 1.3 (Waring et al., 2006). For both
right and humpback whales, serious
injuries and mortalities resulting from
interactions with commercial fishing
gear regulated under the ALWTRP have
occurred, and PBR has been exceeded.
Therefore, NMFS is required to take
additional action to further reduce
serious injury and mortality to large
whales resulting from interactions with
commercial fishing gear regulated under
the ALWTRP. NMFS is trying to find a
balance between allowing the fishing
industry to continue to fish and
protecting the endangered large whales
that are protected under the ALWTRP.
The only way that right whales would
be free of all entanglement and
associated serious injury and mortality
risks due to fishing gear would be to
enact gear closure areas throughout the
species’ range. However, the ALWTRP
regulations favor broad-based gear
modifications over area closures.
Movement and location of whales is
often difficult to predict with certainty,
making gear modifications potentially
more protective than closures of limited
areas. Furthermore, closures may
produce undesirable consequences such
as concentrations of gear just outside of
closed areas, which could increase
entanglement risks to large whales.
Comment 320: Some commenters
argued that the economic viability of
east coast fisheries is at least as
important as whale protection goals.
They were concerned that additional
costly fishery regulations would drive
the fishing industry out of business.
Response: Due to the continued
entanglements of the large whale
species covered under the ALWTRP,
NMFS is required to make further
modifications to the ALWTRP. NMFS
has chosen not to move forward with
implementing new area closures;
therefore, the new regulations favor
broad-based gear modifications. In the
FEIS, NMFS examines the economic,
social, and biological impacts on
commercial fishermen resulting from
the modifications to the ALWTRP under
the final preferred alternative. In
addition, the Final Regulatory
Flexibility Analysis (FRFA) in the FEIS
considers the impacts of the proposed as
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well as final preferred alternatives on
small entities and examines avenues for
reducing the impacts. For further
information on economic issues, see
response to Comment 319.
Comment 321: One commenter asked
if NMFS tested the use of sinking and/
or neutrally buoyant groundline on
Maine’s rocky sea floor to determine
that it is not economically devastating.
Response: NMFS has provided a
number of fishermen along the coast of
Maine, from Lubec to Kittery, with
neutrally buoyant groundline in order
for those fishermen to test at sea the
feasibility of its use in the areas they
fish. NMFS received feedback from
some of these fishermen who fish on a
variety of bottom types, including rocky
bottom, that the line was fished
successfully. Other fishermen reported
that they experienced problems when
using this type of line. It should be
noted that anywhere along the East
Coast, different fishermen are going to
experience different issues with the use
of sinking and/or neutrally buoyant
groundline based on differences in tidal
and weather conditions, gear
configurations, and fishing practices.
Comment 322: One commenter said
that section 118 of the MMPA allows
consideration for the economics of the
gillnet fishery and availability of
existing technology as well as state and
regional FMP’s.
Response: Section 118 (f)(2) of the
MMPA includes both short- and longterm goals. Specifically, it states that
‘‘the immediate goal of a take reduction
plan for a strategic stock shall be to
reduce, within 6 months of its
implementation, the incidental
mortality and serious injury of marine
mammals taken incidentally in the
course of commercial fishing operations
to levels less than the potential
biological removal level established for
that stock under section 117’’ (16 U.S.C.
1387). Further, it states that ‘‘the longterm goal of the plan shall be to reduce,
within 5 years of its implementation,
the incidental mortality or serious
injury of marine mammals incidentally
taken in the course of commercial
fishing operations to insignificant levels
approaching a zero mortality and
serious injury rate, taking into account
the economics of the fishery, the
availability of existing technology, and
existing State or regional fishery
management plans’’ (16 U.S.C. 1387). To
achieve these goals, NMFS determined
that additional modifications to the
ALWTRP were warranted based on the
continued serious injury and mortality
of large whales in commercial fishing
gear. See response to Comment 320.
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Comment 323: One commenter stated
that economic impacts are similar across
the board, with most impact affecting
the New England lobster fishery. The
commenter does not see how NMFS can
justify choosing Alternatives 3 and 6 as
preferred over Alternatives 2 and 4,
based on economic analysis and what is
known about the Mid-Atlantic as a right
whale migratory corridor. Another
commenter also believed New England
lobstermen are also disproportionately
burdened.
Response: Based on comments
received on the DEIS, NMFS has
developed a new preferred alternative,
Alternative 6 Final, that offers
significantly lower economic costs
while sacrificing little protectiveness.
Chapter 8 of the EIS provides an
overview of the costs and benefits of all
the alternatives.
Because of the geographic
concentration of the lobster fishery in
New England (see Chapter 7) and the
relatively large size of the lobster
fishery, it is true that New England
vessels bear a large share of the overall
estimated costs of the ALWTRP
modifications. Given whale movements
and behavior, however, New England
waters represent important areas for
entanglement risk reduction.
Furthermore, the social impact analysis
suggests that under Alternative 6 Final
(Preferred), only a limited subset of
smaller vessels are likely to experience
costs that represent a significant share of
per-vessel fishing revenues. Finally,
groundline buyback programs will help
mitigate compliance cost impacts. See
Comment 137.
Comment 324: One commenter stated
that vessel compliance costs assume
upper and lower bounds of complying
are similar between vessel classes. The
commenter states that, as noted in the
DEIS, this could underestimate some
vessel class revenue estimates and
overestimate compliance cost impacts.
The commenter also believes small
sample sizes of vessel revenues are
insufficient in providing accurate
analysis of potential compliance cost
estimates by vessel class. Therefore, the
commenter requests that these economic
and social impact analyses be corrected
to be more representative.
Response: The commenter correctly
recognizes the uncertainty inherent in
both the cost and revenue analyses and
the efforts made to characterize this
uncertainty. It should be noted,
however, that the direction of this
uncertainty is unknown (i.e., the figures
could be biased in the opposite
direction of those stated by the
commenter). Furthermore, the
shortcomings of the revenue data (e.g.,
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sample sizes for certain vessel classes
and fisheries) are fully documented in
Chapter 7 of the EIS; no better revenue
sources are available at this time.
Comment 325: One commenter
questioned DEIS Exhibit 7.4.1.2, which
specified that vessel revenues were
derived from the 2002 NMFS dealer
database, yet are compared with
compliance costs under future
regulations (and, therefore, the likely
impacts on employment). The
commenter believes analysis is needed
that will project the difference between
the costs and revenues following the
proposed implementation date of the
new rules.
Response: Consistent with the
comment, the analysis of vessel impacts
ideally would compare costs and
revenues following the introduction of
the ALWTRP modifications; instead, the
analysis compares with-regulation costs
to pre-regulation revenues. Little
information exists to assess how the
ALWTRP modifications would affect
vessel revenues; however, the nature
and scale of the proposed regulatory
changes would likely have little impact
on harvests, prices, and other factors
affecting vessel revenue. Therefore, even
if comparison of post-regulatory costs
and revenues were feasible, it is
unlikely that such an analysis would
result in markedly different
socioeconomic impact conclusions.
Comment 326: One commenter said
that the chart in Chapter 6 about
economic analysis left out several
counties and ports in New Jersey (Sea
Isle City, Cape May, Belford, and Point
Pleasant) that should have been
considered in the economic analysis.
The commenter said that all fishermen
affected by the rule in those regions
should be considered in the analysis,
even those listed above that do not meet
the criteria for at risk counties.
Response: The definition of at-risk
communities inherently focuses on
areas where the potential for ALWTRP
impacts is significant in scale, as
indicated by ALWTRP landings or
vessels. As suggested by the commenter,
however, other counties that do not
meet the threshold criteria may realize
significant impacts. Although the
overall scale of these impacts may not
be great, their importance to specific
towns, neighborhoods, or vessels should
not be overlooked. This point has been
highlighted in the FEIS. In addition, the
county-level analysis is intended to
provide a broad idea of where impacts
may be centered geographically. It is
separate from the cost/revenue analysis,
which considers all vessels, regardless
of their landing port or home port.
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Comment 327: One commenter said
that it would probably cost fishermen
$75,000 just to switch over to the rope
plus a couple weeks worth of work. The
costs includes the crew and everything
else.
Response: While the model vessels
analyzed in Chapter 6 of the FEIS are
generalized and may not reflect costs for
all individual vessels, NMFS does not
believe that initial gear conversion costs
(costs beyond routine gear replacement
costs) will typically be as high as
$75,000. The analysis suggests that
average initial investment costs are
likely to be on the order of $39,000 for
offshore vessels. While these vessels
may realize high costs relative to
revenues, fishermen have the option of
seeking loans to finance the initial costs
of converting their gear. In addition,
initial conversion costs may be
mitigated, at least in part, by current
and future groundline buyback
programs operated by NMFS and other
partners.
Comment 328: One commenter
expressed concern with the prices
associated with changing to sinking
rope. The commenter states that rope
was $98 a coil last year and this year it
was $113. Hence, the commenter
believes that the rope price will go up.
The commenter also believes that fuel is
a major issue, stating that as fuel costs
go up, the cost of rope will follow. It
cost $10,000 for the commenter to
switch over his rig in 2004 and in 2008
it may cost $15,000–20,000 or more
depending on the price of fuel. The
commenter also said that China is
buying up all the materials needed to
make this rope. The commenter asked
what will happen in 2008, if the rope
will be available, and the fishermen will
be able to afford the rope.
Response: The commenter is correct
in noting the positive relationship
between oil costs and petroleum-based
materials in groundline as well as the
dynamic nature of oil prices. In the
FEIS, the economic analysis has been
revised to incorporate up-to-date prices
for groundline, fuel, and other input
parameters. Predicting future trends in
oil prices is highly complex, however;
therefore, the analysis does not attempt
to forecast changes in input costs for
future years.
Comment 329: One commenter stated
that he spreads his expenses out over
the year, and to absorb a massive
expense that has been expensed over a
period of 6 or 8 years does not work. A
hundred percent of the burden of the
expense of these requirements goes to
the industry.
Response: The comment focuses
primarily on the large initial investment
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that may be required to convert gear.
Although costs are high for some
vessels, NMFS made modifications to
the final rule, based on public comment,
to decrease costs where possible while
still meeting its goals under the MMPA
and ESA (see Changes from the
Proposed Rule section of the preamble).
While these vessels may still realize
high costs relative to revenues, the
impacts of converting to sinking and/or
neutrally buoyant groundline may be
defrayed, in part, by current and future
groundline buyback programs operated
by NMFS and other partners. In
addition, although the requirements
under Alternative 6 Final (Preferred)
may impose significant costs within the
first year after publication of the final
rule (to convert all groundline to sinking
and/or neutrally buoyant groundline),
fishermen may be able to distribute the
cost of the new gear over its useful life
by seeking a loan. After the first year,
ongoing costs would be significantly
lower as fishermen would only need to
replace worn-out and lost gear.
Comment 330: One commenter said
that NMFS needs to think about social
and economic impact to fishermen
themselves, including the cost to change
things around for fishermen and the
social and economical factors going on.
Response: NMFS is sensitive to the
costs of complying with this final rule
and has characterized the economic and
social impacts in the FEIS. Chapter 7 of
the EIS identifies vessel segments that
may be heavily affected by the
requirements and suggests that under
Alternative 6 Final (Preferred), a limited
number of small vessels are most at risk.
As a result, harvest levels are unlikely
to change and related industries (e.g.,
seafood processing) are not likely to be
affected. Although costs are high for
some vessels, NMFS made
modifications to the final rule, based on
public comment, to decrease costs
where possible while still meeting its
goals under the MMPA and ESA (see
Changes from the Proposed Rule section
of the preamble). While some vessels
may still realize high costs relative to
revenues, fishermen have some options
to try to mitigate these costs. For
example, the impacts of converting to
sinking and/or neutrally buoyant
groundline may be defrayed, in part, by
current and future groundline buyback
programs operated by NMFS and other
partners.
Comment 331: One commenter said
that it has been estimated recently that
the economic benefit of the lobster
fishery in Maine is 500 million dollars.
This commenter stated that it was ironic
that the fishermen were a week away
from paying taxes and the same
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government that supports them is
coming to them with alternatives that
would severely impact, if not end, their
way of life. The commenter said that
Coastal Maine and coastal communities
depend on the lobster fishery as part of
their heritage and culture, as well as an
economic base and there is nothing that
can take its place.
Response: NMFS acknowledges the
economic importance of the lobster
industry and has attempted to
characterize the harvest and processing
sectors accurately in the EIS. The
specific source of the commenter’s $500
million figure is uncertain, but the
estimate is not unreasonable given exvessel revenues and the regional
economic contribution of industries that
depend on fishing. However, the
ALWTRP modifications contained in
the final rule are not likely to have the
severe implications suggested by the
commenter. While costs may be high for
some vessels, the compliance costs are
generally commensurate with revenues,
i.e., costs as a percent of revenue are not
prohibitive. Chapter 7 identifies vessel
segments that may be heavily impacted
by the requirements and suggests that
under Alternative 6 Final (Preferred), a
limited number of small vessels are
most at risk. As a result, harvest levels
are unlikely to change and related
industries (e.g., seafood processing) are
not likely to be affected.
Comment 332: One commenter was
concerned about the economic impacts
of changing over from either neutrally
buoyant rope or going to all sink rope.
The commenter recently bought
neutrally buoyant rope for $1.85/pound
and does not understand where NMFS
got $3,500 per boat cost. A few
commenters believed that cost is too
low, and that money spent on
groundlines alone will be over $20,000.
Response: The per-vessel cost cited
($3,500) is the average across a variety
of vessel size classes and is an
annualized figure; that is, it represents
the sum of annualized initial investment
costs and annual maintenance costs.
Consistent with the comment, the lump
sum initial investment for most lobster
vessels will be higher than annualized
costs. Although costs are high for some
vessels, NMFS made modifications to
the final rule, based on public comment,
to decrease costs where possible while
still meeting its goals under the MMPA
and ESA (see Changes from the
Proposed Rule section of the preamble).
While these vessels may still realize
high costs relative to revenues,
fishermen have some options to try to
mitigate the costs. For example, the
impacts of converting to sinking and/or
neutrally buoyant groundline may be
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defrayed, in part, by current and future
groundline buyback programs operated
by NMFS and other partners. In
addition, although the requirements
under Alternative 6 Final (Preferred)
may impose significant costs within the
first year after publication of the final
rule (to convert all groundline to sinking
and/or neutrally buoyant groundline),
fishermen may be able to distribute the
cost of the new gear over its useful life
by seeking a loan.
Comments on Other Species
Comment 333: One commenter states
that NMFS has not looked at the
impacts on other species and has little
basis to assume humpbacks, finbacks,
and minke whales would benefit. The
commenter states that right whales,
which have different prey requirements,
are the main target of conservation. This
leads to different feeding and
distribution, which may also lead to
different conservation needs. The
commenter believes NMFS should not
rely on closures and gear modifications
that only protect right whales because
the agency may omit areas that are
important to other large whale species.
Response: The ALWTRP is designed
to reduce the risk of mortality and
serious injury to large whales (right,
humpback, and fin whales), with
benefits to non-endangered minke
whales, due to interactions with
commercial fishing gear. The ALWTRP
focuses on reducing entanglements of
critically endangered North Atlantic
right whales, whose population contains
approximately 300 animals. NMFS
established the areas and seasons being
implemented in this final rule by
analyzing databases that included right,
humpback, and fin whale sightings.
NMFS believes that the gear
modifications being implemented,
especially the requirement to use
sinking and/or neutrally buoyant
groundline, will benefit all large whale
species by reducing entanglement risk
of commercial fishing gear. In the
future, NMFS will re-evaluate the
ALWTRP with the ALWTRT if
information becomes available
indicating that the measures being
implemented in this final rule are
ineffective.
Comment 334: One commenter stated
that there is an increase in lobster effort
(800 in 1996 and 1400 today) and gear
conflicts, and a decrease in herring
abundance due to expanded trawling;
therefore, there are fewer humpbacks,
finbacks, and minke whales in Maine
according to an article published in
‘‘Fisherman’s Voice,’’ April 2005.
Response: The information provided
in the article in ‘‘Fisherman’s Voice’’
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with respect to large whales off the coast
of Maine is anecdotal. NMFS does not
estimate the local abundance of
humpback, fin, and minke whale
populations so it is difficult to
determine the local abundance of these
species off the coast of Maine. For
further information on these species,
please see the SAR (Waring et al., 2006).
Comment 335: One commenter
believed that the take levels for some
whale species are so low that they could
not be achieved. This commenter
believed, therefore, that any takes
resulting from whale entanglements in
fishing gear would lead to more
stringent fishery regulations.
Response: Under section 118 of the
MMPA, NMFS is required to meet both
the short and long-term take reduction
plan goals of reducing serious injury or
mortality from commercial fishing
operations. The short-term goal is to
reduce serious injury or mortality to
below PBR, while the long-term goal is
to achieve a level that is approaching a
zero mortality and serious injury rate
(i.e., ZMRG). Due to the continued
entanglements of large whales in
commercial fishing gear, NMFS is
required to take additional action to
further reduce the entanglement risk
associated with commercial fishing gear.
NMFS will continue to discuss with the
ALWTRT any future modifications that
will be made to the ALWTRP.
Comment 336: One commenter states
that NMFS has not updated SARs and
entanglement studies for finbacks or
minke whales. Without scientific
information, the commenter believes
there is no way to assess impacts of
entanglements on these stocks or the
ALWTRP benefits to them.
Response: NMFS recently published
updated SARs for all four of the large
whale species affected by the ALWTRP
(Waring et. al., 2006). Information from
these and earlier SARs has been
integrated into the FEIS.
Comments on Definitions
Comment 337: Some commenters
questioned NMFS’ basis for determining
exempted areas. One commenter asked
how ‘‘frequently’’ is defined in the
DEIS. The commenter specifically
referenced the DEIS language that states
NMFS will re-evaluate exempted areas
if right whales are frequently reported
inside these areas.
Response: NMFS did not define
‘‘frequently’’ in the DEIS. NMFS
believes, based on scientific data, that
endangered large whales will rarely
venture into bays, harbors, or inlets that
have been exempted. Based on this, and
other information provided in Appendix
3–A of the FEIS related to the
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exemption waters in final preferred
alternative, NMFS believes the risk of
gear to large whales in the exempted
areas is minimal. However, NMFS will
continue to monitor all exempted areas,
and encourage states to develop
contingency plans for large whales in
these areas. Should new information
become available that indicates that a
change in the inshore or deep water
exemption areas is warranted, NMFS
will share the information with the
ALWTRT and take appropriate action.
Comment 338: One commenter
requested that NMFS define ‘‘weighted
device’’ for enforcement purposes (i.e.,
‘‘include a weak link on all flotation
and/or weighted devices attached to the
buoy line’’).
Response: NMFS agrees and has
modified the regulatory text to identify
acceptable ‘‘weighted devices’’. For
example, a weighted device includes
window weights, but does not include
traps/pots, gillnets, anchors, or leadline
woven into buoyline.
Comment 339: One commenter does
not support the definition of a set
gillnet, which is considered an
anchored gillnet, and suggests a
definition of a set gillnet as ‘‘any gillnet
that is weighted, but does not have an
anchor(s) on either end and returns to
port with the vessel’’.
Response: Although various types of
gillnets are included in the anchored
gillnet definition, such as set and stab
nets, NMFS recognizes that the nets may
be fished in various ways. This issue is
of particular relevance in the MidAtlantic. NMFS will discuss this with
the ALWTRT and coordinate with other
TRTs that may use this definition under
section 229.2 to determine whether this
type of change to the definition is
appropriate.
Comment 340: One commenter stated
that the proposed definition of wet
storage of gear in the proposed rule at
paragraph (c)(ii) on page 35922 (70 FR
35894, June 21, 2005) is not enforceable
as currently written. The definition
specifies that trap or pot gear must be
hauled out of the water at least once
every 30 days. The commenter is
concerned that to prove this portion of
the rule, an unsustainable amount of
surveillance would be required to
maintain visual proximity of a
particular piece of gear.
Response: Thirty-day soak limits have
been enforced. Enforcement actions
based on the 30-day soak limit were
taken in 10 cases in 2005.
Comment 341: NMFS received one
comment regarding the definition of
weak links on page 35922 (ii)(B)(1) of
the proposed rule (70 FR 35894, June
21, 2005). The commenter states that
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USCG personnel will be unable to
determine the breaking strength of any
type of weak link unless the breaking
strength is clearly indicated by the
manufacturer.
Response: NMFS believes that the
weak link requirements are enforceable.
In the regulations, NMFS references a
brochure that outlines the weak link
techniques currently approved to assist
in compliance with and enforcement of
the regulations, and specifies how to
obtain the brochure. NMFS has worked
with the USCG in the past to provide
training and tools for enforcement
efforts. NMFS will continue to provide
necessary additional training and tools
to the USCG to support enforcement of
the ALWTRP.
Comment 342: NMFS received one
comment regarding the definition of
tending/anchoring/weak links on page
35927, (ii)(c), of the proposed rule (70
FR 35894, June 21, 2005). This section
states that all gillnets must return to
port with the vessel unless the gear
meets the required specifications. The
commenter states that a USCG officer
has no way of determining whether insitu gear is in compliance with weak
link or anchoring requirements. To
enforce this, a law enforcement officer
would need to be present during gear set
or retrieval. Additionally, the
commenter states that some
requirements (e.g., breaking strength)
may be impossible to determine on
scene, undermining the intended effect
of this regulation.
Response: Although the ALWTRP
regulations are complex, NMFS believes
they are enforceable. NMFS has worked
with the USCG in the past to coordinate
during the development of regulations,
and as well as to provide training as
noted in the response to Comment 341.
Additionally, NMFS will work with the
USCG on a coordinated plan to facilitate
enforcement of the ALWTRP.
Comment 343: NMFS received one
comment regarding the definition of
gear requirements on page 35923 (iii)(B)
of the proposed rule (70 FR 35894, June
21, 2005), specifically ‘‘No person may
fish with or have available for
immediate use trap/pot gear.’’ The
commenter suggested clearly defining
the term ‘‘available for immediate use’’
for law enforcement personnel. The
commenter stated that a good example
is found in enforcement of Turtle
Excluder Devices (TEDs), where
shackling the trawl to the doors is
indicative of ‘‘available for immediate
use’’. Without amplifying information,
the commenter believes that arbitrary
and capricious enforcement may result.
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Response: NMFS agrees and has
modified the regulatory text to address
this issue.
Comment 344: NMFS received one
comment regarding the definition of
‘‘groundline’’ on page 35923 (5)(ii)(B) of
the proposed rule (70 FR 35894, June
21, 2005). That section states that all
groundlines must be composed entirely
of sinking or neutrally buoyant line
unless exempted. The commenter states
that if this line is not labeled as sinking
or neutrally buoyant, it will not be
recognized as a violation. A USCG
boarding officer will only see the line
coiled on deck or under strain as it is
in the process of being hauled back or
set and neither condition will
demonstrate compliance with the
regulation.
Response: In this final rule, NMFS is
amending the definitions of ‘‘neutrally
buoyant line’’ and ‘‘sinking line’’ and is
clarifying each definition in relation to
groundlines and buoy lines. Also, to
provide a clearer definition of neutrally
buoyant and sinking line, NMFS has
developed criteria for establishing a
density standard for neutrally buoyant
and sinking line and used these criteria
to develop the definitions. NMFS will
finalize a procedure for assessing the
specific gravity of line, which NMFS
will use in the future to determine
whether a manufactured line meets the
accepted density standard, through this
final action. Additionally, NMFS is
developing guidance for law
enforcement officers on how to evaluate
whether line is sinking/neutrally
buoyant or floating in the field.
Comment 345: NMFS received one
comment regarding the definition of
‘‘anchoring system’’ on page 35926
(ii)(C) of the proposed rule (70 FR
35894, June 21, 2005). The commenter
believes the requirement to have a
burying anchor is easily enforceable, but
it will be difficult to determine if the
different types that will be encountered
will have a holding capacity equal to or
greater than a 22-lb (10.0-kg) Danforthstyle anchor. The commenter suggested
providing the USCG with a table that
identifies all the anchoring systems of
these types that meet the holding
capacity requirement.
Response: NMFS believes that the
anchoring requirements are enforceable.
In the regulations, NMFS references a
brochure that outlines how to comply
with any anchoring requirements to
assist in compliance with and
enforcement of the regulations, and
specifies how to obtain the brochure.
NMFS has worked with the USCG in the
past to provide training and tools for
enforcement efforts. NMFS will
continue to provide any necessary
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additional training and tools to the
USCG to support enforcement of the
ALWTRP.
Comment 346: NMFS received one
comment regarding the definition of
‘‘night’’ on page 35932 of the proposed
rule (70 FR 35894, June 21, 2005). The
commenter suggests changing the
definition to ‘‘Night means, with
reference to the regulated waters of
Georgia and Florida, any time after
official sunset and before official sunrise
as determined for the date and location
in the nautical Almanac, prepared by
the U.S. naval Observatory’’.
Response: NMFS proposed definitions
of sunset and sunrise that referenced the
National Almanac, prepared by the U.S.
Naval Observatory. However, since
proposing definitions in 50 CFR 229.2
for ‘‘sunrise’’ and ‘‘sunset’’, these
definitions were added through the
BDTRP (71 FR 24776, April 26, 2006).
Thus, the definitions in 50 CFR 229.2
are as follows: ‘‘Sunrise means the time
of sunrise as determined for the date
and location in the Nautical Almanac,
prepared by the U.S. Naval
Observatory;’’ and ‘‘Sunset means the
time of sunset as determined for the
date and location in the Nautical
Almanac, prepared by the U.S. Naval
Observatory.’’ NMFS believes that these
modifications will make the ‘‘night’’
definition clearer and more enforceable.
Comment 347: One comment was
received regarding the definition of
special provision for strike nets on page
35929(5)(i)(A) of the proposed rule (70
FR 35894, June 21, 2005). This
paragraph states that no nets can be set
at night when visibility is less than 500
yards (457.2 m or 1,500 ft). The
commenter believes this would be
subjectively enforced. The commenter
recommended less subjective language
(e.g., ‘‘No nets may be set after official
sunset as determined for the date and
location in the Nautical Almanac,
prepared by the U.S. Naval
Observatory’’).
Response: The regulations require,
amongst other requirements, that no
nets are set at night or when visibility
is less than 500 yards (1500 ft, 457.2 m).
Night is currently defined under 50 CFR
229.2 as any time between one half hour
before sunset and one half hour after
sunset. Through this final rule, NMFS is
defining sunset and sunrise by
referencing the Nautical Almanac
prepared by the U.S. Naval Laboratory.
Clarification Requests for the FEIS
Comment 348: One commenter asked
if the RPA measures (developed
pursuant to ESA section 7) contained in
the DEIS alter the reasonable and
prudent measures that have previously
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been incorporated into the ALWTRP
through past rulemakings.
Response: The measures described in
the DEIS were developed by NMFS
through feedback received during
meetings with the ALWTRT, as well as
through public scoping and comment,
not as a result of a section 7
consultation on any Federal action. A
section 7 consultation has been
reinitiated to examine the effects of the
Federal lobster fishery, as modified by
the existing ALWTRP and RPA for right
whales. This consultation is in progress.
NMFS has also reinitiated consultation
on the continued implementation of the
Federal summer flounder, scup, and
black sea bass fisheries that are managed
under the Summer Flounder, Scup, and
Black Sea Bass FMP, based on new
information that suggested effects to
listed species as a result of the black sea
bass and scup trap/pot fisheries in a
manner or to an extent not previously
considered. This consultation is
ongoing. NMFS will consider the
provisions of this final rule during
consultation on the continued
implementation of the Summer
Flounder, Scup, and Black Sea Bass
FMP. NMFS will also consider, based
on the criteria for reinitiating
consultation (50 CFR 402.16), whether
formal consultation for the continued
implementation of the Northeast
Multispecies, Monkfish, and Spiny
Dogfish FMPs must be reinitiated as a
result of the changes to the ALWTRP.
Section 7 consultations completed June
14, 2001, on the continued
implementation of these FMPs
concluded that the fisheries would
jeopardize the continued existence of
right whales. An RPA was provided,
and the regulatory components were
implemented as part of the ALWTRP.
NMFS has determined that the
operation of other federally-managed
fisheries (e.g., HMS, Coastal Pelagics,
Snapper/Grouper) will not jeopardize
the continued existence of right whales
or any other large whale species
managed under the ALWTRP.
Comment 349: One commenter asked
NMFS to discuss the need for additional
ESA section 7 consultations to address
the potential impacts of the revised
ALWTRP on right whales and other
listed species in the FEIS.
Response: An informal consultation
under the ESA was concluded for the
rule to modify the Atlantic Large Whale
Take Reduction Plan on December 21,
2004. As a result of the informal
consultation, the Regional
Administrator determined that the
measures to modify the ALWTRP are
not likely to adversely affect ESA-listed
cetaceans, sea turtles, fish, or critical
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habitat that occur within the area
affected by the rulemaking.
Modifications are being made to the
ALWTRP by this final rule to more
broadly address the incidental
entanglement of large whales in fishing
gear that result in serious injury and
mortality. Some of these modifications
(e.g., regulating additional trap/pot and
gillnet fisheries under the ALWTRP,
requiring the broad-based use of sinking
and/or neutrally buoyant groundline)
are expected to have an effect on ESAlisted species. However, depending on
the species, all of the effects are
expected to be either beneficial or
negligible.
Comment 350: One commenter said
that on p. 3–6 of the DEIS, the driftnet
provisions needed to be clarified.
Response: NMFS has made a variety
of edits and clarifications in Chapter 3
of the FEIS that may better characterize
proposed changes for driftnet vessels.
Comment 351: One commenter asked
NMFS to clarify DEIS pg. 5–40; as the
commenter detected a contradiction
between whale distribution and when
the requirements are required.
Response: NMFS disagrees. The
alternatives under consideration in the
DEIS considered whale distribution
when determining the time periods of
the requirements. Although whales may
be present outside a seasonal window,
the sightings are rare, and the risk of
gear to large whales at these times of the
year is minimal. However, NMFS will
continue to monitor the areas where
seasonal requirements are in effect.
Should new information become
available that indicates that a change in
seasonal window is warranted, NMFS
will share the information with the
ALWTRT and take appropriate action.
See response to Comment 41.
Comment 352: One commenter states
that the hazards to whales and areas of
most risk need to be clarified.
Response: The ALWTRP regulations
favor broad-based gear modifications
over additional special management
areas. Movement and location of whales
is often difficult to predict with
certainty. However, as NMFS continues
to conduct rulemaking to achieve the
goals of the ALWTRP, special
management areas could be defined in
the future.
Comment 353: Some commenters
urged NMFS to include a discussion in
the FEIS about the effectiveness of weak
links because they are treated as an
important risk reducing element, but
effectiveness is still unclear. One
commenter states that in the DEIS,
NMFS indicates the agency believes
weak links might work, but does not
provide data or analysis on how
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frequently weak links have failed to
prevent entanglements in cases for
which gear was examined. Another
commenter stated that the DEIS leaves
a false impression that weak links are
known to be effective in reducing
entanglements and that using such
devices would reduce bycatch to
required PBR levels.
Response: NMFS has added
additional clarification in the FEIS on
these issues regarding weak links.
Evidence that weak links help prevent
whale entanglements is discussed in
Chapter 5, Section 5.1.1.3 of the FEIS.
Section 5.2 discusses impacts on nonwhale species and explicitly
acknowledges that weak links are not
likely to reduce bycatch of most nonwhale species; only whale species with
the size/strength to break weak links are
likely to benefit from weak link
requirements.
Comment 354: One commenter states
that the DEIS is incorrectly describing
collaborative real and simulated fishing
and field tests conducted by fishermen
and the NMFS gear research team as
‘‘simulated whale entanglements’’.
Response: A search of the entire EIS
document yielded no instances of the
term ‘‘simulated whale entanglements’’.
However, NMFS did find a discussion
in the footnote of Chapter 5 of the DEIS
describing NMFS investigations
‘‘simulating an entanglement.’’ NMFS
believes that the characterization of the
studies as written is appropriate.
Comment 355: One commenter
referenced page 2–39 of the DEIS, in
which NMFS reports that 9 fatal
entanglements and 22 live
entanglements of large whales were
observed in 2002, after the most recent
revisions of the ALWTRP. The
commenter requested that NMFS
address this in the FEIS, as caveats were
not taken into account in the DEIS.
Response: Data on entanglements
occurring since the most recent
revisions to the ALWTRP have been
updated using finalized figures
published in the 2003 Stock Assessment
Report (Waring et al., 2006). Apart from
the general caveats applying to all
entanglement information, additional
caveats are no longer appropriate.
Comment 356: One commenter states
that the DEIS does not provide the
history or context of right whale status
relative to federal efforts to protect
whales and fails to consider cumulative
effects of all sources of mortality on
right whales.
Response: NMFS disagrees. The DEIS
and FEIS provide a status of right
whales (Chapter 4—Affected
Environment), as well as a cumulative
effects analysis (Chapter 9—Cumulative
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Effects Analysis) that considers various
sources of mortality to right whales,
including the following sources of
mortality: commercial whaling, ship
strikes, water pollution, noise pollution,
climate change, and prey availability.
Changes From the Proposed Rule
NMFS made the following changes
from the proposed rule published on
June 21, 2005 (70 FR 35984, June 21,
2005) to the final rule:
(1) The proposed rule requirement for
sinking and/or neutrally buoyant
groundline by January 1, 2008, for trap
pot gear (70 FR 35900, June 21, 2005)
and gillnet gear (70 FR 35904, June 21,
2005) (unless otherwise required in the
Cape Cod Bay Restricted Area for trap/
pot (January 1–May 15) or SAM areas)
is modified in this final rule to be
effective twelve months after
publication of the final rule. NMFS
believes that the January 1, 2008,
deadline will not give fishermen time to
comply with this requirement.
Typically, NMFS provides 30 or 60 days
for fishermen to comply with gear
modifications such as mesh size
restrictions and other requirements.
However, as evident by overwhelming
public comment, given the magnitude of
the time and resources needed by
fishermen to change their gear to
sinking and/or neutrally buoyant
groundline requirement, NMFS believes
giving fishermen 12 months from the
publication of the final rule to comply
is warranted.
Although the broad-based sinking/
neutrally buoyant groundline
requirement will become effective on
October 6, 2008 (except in the Cape Cod
Bay Restricted Area for trap/pot
(January 1–May 15) and expanded SAM
areas), NMFS believes the time frame
allowed for this requirement will not
compromise conservation efforts. As
stated in the proposed rule, NMFS
believes that fishermen will begin
changing over their gear prior to the
effective date as fishermen replace their
groundline as it naturally wears out and
due to previous or planned groundline
exchange programs.
The early changeover is also likely to
continue particularly in the northeast as
fishermen respond to gear modifications
required by the implementation of SAM
and DAM programs, which require
seasonal or temporary use of nonfloating groundline. For example, some
fishermen may choose to fish with SAM
and/or DAM compliant gear year round,
or at least during the months when SAM
areas are in effect and DAM zones are
most likely to be triggered, rather than
having to change their gear over when
a SAM area is effective or remove it
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when a DAM zone is established. NMFS
believes this situation will occur in
other areas too, especially as fishermen
replace their old line with new line,
which would begin to provide increased
protection of large whales from
entanglement earlier than twelve
months from the publication of this
final rule.
(2) Modifications to the proposed
exempted areas in Maine (70 FR 35906,
June 21, 2005) are approved in this final
rule. In 2003, the State of Maine asked
NMFS to re-examine the ALWTRP
exemption lines and Maine DMR
submitted a suggested exemption line to
the agency. As described in the
proposed rule, NMFS chose what it felt
at the time was a more conservative
exemption line for the State of Maine.
However, NMFS received a number of
comments from members of the fishing
industry and government agencies in
support of this line, stating a lack of
sightings data inside the suggested line.
Based upon these comments, NMFS has
further investigated the exemption line
suggested by the State of Maine and its
level of protection. NMFS reanalyzed
the current and proposed exemption
lines and analyzed large whale sightings
distribution data from available sources
that are more current than the
information analyzed for the DEIS.
NMFS re-examined dedicated survey
effort and opportunistic sightings data
from 1960 to mid-September 2005,
obtained from the NARWC Sightings
Database (curated by URI),
supplemented by additional data on
humpback and fin whale sightings. In
addition, NMFS analyzed large whale
sightings data from 2002 through 2006
that were collected through the NEFSC’s
systematic aerial surveys, as well as
through the Northeast U.S. Right Whale
Sighting Advisory System (SAS). NMFS
also analyzed a right, humpback, and fin
whale sightings database compiled by
Maine DMR, which includes sightings
reported by Maine Marine Patrol, whale
watching companies, etc. Lastly, NMFS
considered right whale satellite tracking
data as provided in peer-reviewed
papers by Mate et al. (1997) and
Baumgartner and Mate (2005).
Sightings and satellite tracking data
along the east coast indicated that
endangered large whales rarely venture
into bays, harbors or inlets. Based on
this, and other information provided in
Appendix 3–A of the FEIS related to the
exempted waters under the final
preferred alternative, NMFS believes
large whales rarely occur inside many of
Maine’s bays, harbors, or inlets.
Although NMFS’ proposed exemption
line was closer to shore in some areas,
NMFS believes Maine DMR’s suggested
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exemption line would adequately
protect endangered large whales. Thus,
NMFS concluded that the final
exemption line for Maine (as suggested
by Maine DMR) is appropriate based on
the current, available information.
Therefore, in this final rule, NMFS is
finalizing the exemption line in Maine
as the line suggested by Maine DMR,
and from this point forward will refer to
this line as the final exemption line for
Maine.
In response to industry comments,
NMFS will not use the 72 COLREGS
line to mark exempted waters for Casco
Bay. Also, NMFS will not use the
territorial sea baselines to exempt Little
River, Pleasant Bay, Narraguagus Bay,
Pigeon Hill Bay, Frenchman Bay,
Muscongus Bay, Johns Bay, or Saco Bay.
Lastly, as proposed, to exempt
Penobscot and Blue Hill Bays, NMFS
will use three coordinates from NMFS’
proposed exemption line for Maine that
match three coordinates from the
exemption line suggested by Maine
DMR. For the remaining inlets in Maine,
the coordinates proposed by NMFS will
be removed and replaced with the
coordinates of the final exemption line
for Maine (Figure 4).
NMFS understands that large whales
may occasionally be reported in
exempted waters, which is consistent
with the sightings data that were
analyzed. NMFS will continue to
monitor all exemption areas, and should
new information become available,
determine if changes to exemption areas
are warranted.
In New Hampshire, waters currently
exempted from the ALWTRP regulations
are those landward of the first bridge
over any embayment, harbor, or inlet.
Through this final rule, NMFS is
modifying the exempted waters for New
Hampshire’s three harbors, two as
proposed and one slightly modified. As
proposed, NMFS will exempt Rye and
Hampton Harbors according to the lines
drawn across the headlands that mark
their entrances to the sea. Portsmouth
Harbor will not be exempted according
to the 72 COLREGS demarcation line
(the only 72 COLREGS line found in the
state) because it will be exempted
through the final exemption line for
Maine, as this line’s final coordinate is
located at Odiorne Point, New
Hampshire.
(3) The proposed exemption lines for
Massachusetts (70 FR 35906, June 21,
2005) are not implemented in this final
rule. This is based on public comments
from the Massachusetts Division of
Marine Fisheries, which indicated that
the proposed exemption lines are too
small to benefit fishermen. In addition,
Massachusetts commercial trap/pot
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57165
fishermen are already using sinking
and/or neutrally buoyant groundline.
Thus, NMFS will not be implementing
the proposed exempted lines at this
time, and will revert back to the status
quo for this area as depicted in Figure
5 (i.e., exempted waters are landward of
the first bridge over any embayment,
harbor, or inlet). If the Massachusetts
Division of Marine Fisheries believes
exemption lines are warranted at some
point in the future, NMFS will revisit
this issue with the ALWTRT.
(4) The final rule will modify the
exempted areas for Long Island Sound
and Gardiners Bay. Regarding the
current Long Island Sound exemption
line, the States of Connecticut and New
York, as well as members of the fishing
industry, cited safety issues and gear
loss concerns with using sinking and/or
neutrally buoyant groundline in an area
just outside of this line, as well as lack
of consistency with other exemptions
lines. Thus, they supported an
exemption line extending north to south
through Block Island Sound from Watch
Hill Point, Rhode Island, to Montauk
Point, New York (following the
territorial sea baseline), based on the
lack of whale sightings in the area and
the need for consistency with
exemption lines in other areas. NMFS
believes this area has infrequent whale
sightings and was able to confirm this
by re-examining dedicated survey effort
and opportunistic sightings data from
1960 to mid-September 2005, obtained
from the NARWC Sightings Database
(curated by URI), supplemented by
additional data on humpback and fin
whale sightings. In addition, NMFS
analyzed large whale sightings data
from 2002 through 2006 that were
collected through the NEFSC’s
systematic aerial surveys, as well as
through the Northeast U.S. Right Whale
Sighting Advisory System, and the right
whale satellite tracking information
provided in Mate et al. (1997) and
Baumgartner and Mate (2005). In
addition, the Riverhead Foundation for
Marine Research and Preservation
recently conducted aerial surveys of the
waters off Long Island, New York and
east of Block Island from November
2004 to April 2005 (RFMRP, 2005). No
large whales were sighted near the
entrance to Long Island Sound or
Gardiners Bay, further confirming that
this area is not important large whale
habitat.
Under this final rule, NMFS will
modify exempted areas for Long Island
Sound and Gardiners Bay by using the
territorial sea baseline that extends from
Watch Hill Point, Rhode Island to
Montauk Point, New York, through
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Block Island Sound, as depicted in
Figure 5.
(5) Components of the buoy line gear
marking requirement in the proposed
rule (70 FR 35905, June 21, 2005) are
being implemented in this final rule.
Although many commenters support the
concept of gear marking, NMFS received
numerous comments opposing the
proposed gear marking scheme stating
that it would be too time-consuming,
costly, impractical to implement while
at sea, and would provide limited
information. Based upon these
comments, under this final rule, all
fisheries will mark with one mark midway on the buoy line in the water
column (i.e., status quo scheme for
previously regulated and newly
regulated fisheries) and mark surface
buoys. NMFS will continue to discuss
gear marking strategies with the
ALWTRT.
(6) The proposed rule configuration
for gillnet net panel weak links (70 FR
35901, June 21, 2005), as well as the
configuration suggested by the public,
will be implemented under this final
rule. NMFS sought comment from the
public on additional configurations for
gillnet net panel weak links and
received numerous, consistent
comments from the fishing industry,
Mid-Atlantic Fishery Management
Council (MAFMC), scientists,
conservationists, and a state
organization regarding an alternate
configuration. The public proposed an
alternative weak link configuration to
the proposed configuration and
placement of five or more weak links/
gillnet net panel. This configuration is
similar to the configuration agreed upon
by consensus by the Mid/South Atlantic
ALWTRT Subgroup at the 2005 meeting.
NMFS believes this alternative
configuration is a functional equivalent
to what was originally proposed. As
gillnet net panels are closely strung
together, a single weak link placed
between the floatline tie loops between
gillnet net panels would provide the
same risk reduction as a single weak
link placed as close as possible to each
end of the gillnet net panel just before
the floatline meets the up and down
line. For this alternative configuration,
weak links would also be required at the
ends of each string where the floatline
tie loop attaches to the bridle, buoy line,
or groundline (depending on how the
gear is configured). Thus, in addition to
the proposed configuration, NMFS will
allow the following: one weak link
placed between the floatline tie loops
between gillnet net panels; one weak
link in the center of each gillnet net
panel; one weak link in the up and
down lines of gillnet net panels; and
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one weak link placed where the
floatline tie loops attaches to the bridle,
buoy line or groundline at each end of
the string. In this final rule, NMFS will
specify the two configurations options
for gillnet net panel weak links where
more than one weak link is required per
gillnet net panel in the associated
ALWTRP management areas (e.g., SAM
areas, Other Northeast Gillnet Waters).
The same configuration option would be
required for all gillnet net panels in a
string.
Based on the determination that the
two net panel weak link configurations
are functional equivalents, NMFS
believes the optional configuration
should be allowed in the current SAM
areas and established DAM zones when
a gear modification option is selected
thirty days after publication of this final
rule. This will allow fishermen to
choose between options without waiting
six months after publication of the final
rule when the SAM area is expanded
and the two configuration options are
allowed in this area. Additionally, this
will allow fishermen to choose between
options in implemented DAM zones
when a gear modification option is
selected. By allowing the two
configuration options in the current
SAM areas earlier than six months after
publication of the final rule, and in
established DAM zones while the DAM
program remains in effect, would reduce
the burden to fishermen by giving them
options for meeting the net panel weak
link requirements without increasing
entanglement risks.
(7) The gillnet weak link and
anchoring configurations from the
proposed rule, as well as an optional
configuration for North Carolina, are
being implemented in this final rule. In
the proposed rule, NMFS sought
comment on alternative weak link and
anchoring configurations within 300
yards (900 ft or 274.3 m) of the beach
(70 FR 35901, June 21, 2005). NMFS
received numerous, consistent
comments from the North Carolina
Division of Marine Fisheries, North
Carolina Division of Coastal
Management, North Carolina Marine
Fisheries Commission (NCMFC),
MAFMC, fishing industry and
conservationists regarding an alternate
configuration for gillnet net panel weak
links and anchoring systems. This
configuration is similar to the
configuration agreed upon by consensus
by the Mid/South Atlantic ALWTRT
Subgroup at the 2005 meeting. NMFS
believes this alternative weak link and
anchoring configuration is a functional
equivalent to what was proposed. Thus,
in addition to the final configuration of
five or more 1,100-lb (499.0-kg) weak
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links per gillnet net panel depending on
the length of the net anchored with the
holding capacity equal to or greater than
a 22-lb (10.0-kg) Danforth-style anchor
on each end of the net string, NMFS will
allow the following within 300 yards
(900 ft or 274.3 m) of the beach along
the shoreline of North Carolina: five or
more 600-lb (272.2-kg) weak links
depending on the length of the net
anchored on the offshore end of the net
string with the holding capacity equal to
or greater than an 8-lb (3.6-kg) Danforthstyle anchor and at the inshore end of
the net string with a dead weight equal
to or greater than 31 lb (14.1 kg). NMFS
will also clarify that the entire net string
must be less than 300 yards (900 ft or
274.3 m) from shoreline for this
provision.
In April 2005, the NMFS Gear Team
worked with a North Carolina
commercial fisherman to conduct an
investigation of weak links and
anchoring systems that would allow
fishermen safe retrieval of gear in
coastal waters within 300 yards (900 ft
or 274.3 m) of the shoreline while
ensuring weak links placed in gillnet
net panels would perform as designed.
These tests were conducted as industry
expressed concern that anchors in the
22-lb (10.0-kg) Danforth range used on
net strings present safety issues for
small vessels. Several types of
anchoring systems and weak link
breaking strengths were examined
during the investigation. Based on
results of the testing, NMFS believes
that allowing an 8-lb (3.6-kg) Danforthstyle anchor on the outside end of the
net string, a 31-lb (14.1-kg) dead weight
on the inside end of the net string along
with 600-lb (272.2-kg) weak links will
allow for a safer anchoring configuration
for coastal fishermen in North Carolina
and provide the same level of protection
to whales as a 22-lb (10.0-kg) Danforthstyle anchor and 1,100-lb (499.0-kg)
weak links.
(8) An exemption for gillnet net panel
weak link and anchoring requirements if
the depth of the float-line is in waters
deeper than 280 fathoms (1,680 ft or
512.1 m) is implemented in this final
rule. Based on public comments, this
final rule will exempt fishermen from
ALWTRP requirements in waters deeper
than 280 fathoms (1,680 ft or 512.1 m)
as whales are not likely to occur in
those depths. Additionally, NMFS has
not tested the operational feasibility of
using weak links in gillnets set to those
depths. This exemption is consistent
with gillnet groundline exemptions
deeper than 280 fathoms (1,680 ft or
512.1 m).
(9) Although NMFS proposed the use
of VMS in lieu of the 100-percent call-
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in requirement for observer coverage in
the ‘‘Southeast U.S. Monitoring Area,’’
from 32°00′ N. lat. to 26°46.5′ N. lat.,
NMFS is modifying the boundaries of
this area to exclude the Southeast U.S.
Restricted Area. Thus, the area would
extend from 27°51′ N. lat. to 26°46.5′ N.
lat. landward of 80°00′ W. long.
Information obtained by NMFS since
the proposed rule was published
indicates that distinguishing between
vessels that are fishing with strikenet
(referred to from this point onward as
gillnet that is deployed so that it
encloses an area of water) versus those
that are fishing with driftnets may be
more difficult using VMS-generated
tracks than originally thought, and VMS
tracks may be ‘‘spoofed’’ (one fishing
technique deliberately made to appear
like another fishing technique) making
it difficult to differentiate between the
two fishing techniques. Distinguishing
between gillnet that is deployed so that
it encloses an area of water and driftnet
fishing is essential since fishing with
gillnet that is deployed so that it
encloses an area of water is allowed in
the restricted area, but fishing with
driftnets is prohibited. Therefore, NMFS
believes a total reliance on VMS to
enforce the time/area gillnetting and
gear-type restrictions of the Southeast
U.S. Restricted Area may be less riskadverse to right whales than monitoring
fishing activities using 100 percent
observer coverage. Observer monitoring,
while not an enforcement tool, can
provide information to managers on
whether regulations need to be modified
to address compliance issues. This
requirement is effective 30 days after the
publication of the final rule rather than
six months after the publication as
proposed, as this would eliminate an
additional requirement for fishermen in
this area.
(10) The proposal for drift gillnet gear
to place one 1,100-lb (499.0-kg) weak
link per gillnet net panel when fishing
tended drift gillnet gear at night is not
accepted in this final rule. NMFS is not
implementing this requirement at this
time as potential safety issues were
raised by the industry and the MidAtlantic Fishery Management Council.
Thus, NMFS believes further research
on this fishery, and specifically testing
weak links in drift gillnet gear, is
needed before weak links should be
required. Thus, this final rule will
implement the current drift gillnet
fishing requirements for the Mid/South
Atlantic and Northeast.
(11) The proposal for trawls of four or
fewer traps to be allowed only one buoy
line (Northern Nearshore Trap/Pot
Waters, Stellwagen Bank/Jeffreys Ledge
Restricted Area, and Federal Waters of
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Cape Cod Bay Restricted Area (May
16—Dec. 31) (70 FR 35899, June 21,
2005)) is not approved in this final rule.
NMFS believes this modification does
not address the current inconsistencies
regarding this requirement both within
the ALWTRP regulations and with the
Federal lobster regulations. NMFS will
address this issue with the ALWTRT
during future discussions regarding
vertical line risk reduction. Thus, the
final rule will continue to implement
the current requirement of trawls of five
or fewer traps to be allowed only one
buoy line in the areas noted above.
(12) The LMA 3/5 (i.e., overlapping
zone between LMA 3 and LMA 5) will
be added to the regulations wherever
LMA 3 is listed in this final rule. This
overlap is based on the final rule
published on March 14, 2006 (71 FR
13034), to amend regulations to modify
the management measures applicable to
the Federal American lobster fishery.
The ALWTRP regulated waters in this
overlap area were originally included in
Lobster Management Area 3 and will be
managed in the same manner. The
addition of LMA 3/5 to the regulations
allows NMFS to have consistency
between the ALWTRP and Federal
lobster management area regulations
where appropriate.
(13) Changing the southern boundary
of the Mid/South Atlantic Gillnet
Waters and the northern boundary of
the Other Southeast Gillnet Waters
management areas from 32°00′ N. lat. to
‘‘South Carolina/Georgia border’’ is not
approved in this final rule (70 FR 35902,
June 21, 2005). NMFS believes that the
32°00′ N. lat. coordinate is more
appropriate to denote the border. Thus,
reverting back to the status quo for this
issue is appropriate.
(14) NMFS received numerous
comments from the fishing industry
stating that the proposed name changes
and area boundaries for Southeast
gillnet management areas were
confusing. Thus, the proposal to change
the terminology of ‘‘Southeast U.S.
Restricted Area’’ to ‘‘Northern
Monitoring & Restricted Area,’’ and the
portion of the ‘‘Southeast U.S. Observer
Area,’’ not included in the ‘‘Southeast
U.S. Restricted Area,’’ to ‘‘Southern
Monitoring Area’’ (70 FR 35908, June
21, 2005) for the Southeastern U.S.
Atlantic shark gillnet fishery only, is not
approved in this final rule.
Additionally, the proposal to have
‘‘Other Southeast Gillnet Waters’’ be a
management area for the Southeast
Atlantic gillnet fishery only, is not
approved in this final rule. NMFS will
extend management areas in the
southeast to the eastern edge of the EEZ
as proposed. Thus, designated waters in
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57167
the Southeast will also be redefined
under this final rule.
NMFS will retain Southeast U.S.
Restricted Area terminology established
in the June 25, 2007 final rule amending
the ALWTRP (72 FR 34632) for both
Southeast Atlantic and Southeastern
U.S. Atlantic shark gillnet fisheries.
Additionally, for the Southeastern U.S.
Atlantic shark gillnet fishery, NMFS
will also change ‘‘Southeast U.S.
Observer Area’’ to ‘‘Southeast U.S.
Monitoring Area’’ for regulated waters
west of 80°00′ W. long., but this area
will now only extend from 27°51′ N. lat.
south to 26°46.5′ N. lat. and VMS will
be substituted for the 100-percent call in
requirement for this area only. Although
100-percent observer coverage would no
longer be required under this final rule,
NMFS would retain observer coverage
sufficient to produce statistically
reliable results to evaluate the impact of
the fishery on protected species. In
addition, this final rule will also define
the waters east of 80°00′ W. long. from
32°00′ N. lat. south to 26°46.5′ N. lat.
and out to the eastern edge of the EEZ
as ‘‘Other Southeast Gillnet Waters.’’
NMFS will designate ‘‘Other Southeast
Gillnet Waters’’ from 32°00′ N. lat. south
to 27°51′ N. lat. for the Southeast
Atlantic gillnet fishery, and south to
26°46.5′ N. lat. for the Southeast U.S.
shark gillnet fishery. The expansion of
this area east to the eastern edge of the
EEZ will be consistent with the
ALWTRP area boundary expansion in
the Mid-Atlantic.
As designated waters have been
redefined, associated requirements in
some waters are being changed under
this final rule. A recent analysis has
found that it is unlikely that large
whales, right whales in particular,
extend eastward beyond 80°00′ W. long.
in the Southeast region. Hence, less
restrictive ALWTRP measures will be
required in ‘‘Other Southeast Gillnet
Waters’’ east of 80°00′ W. long. and out
to the eastern edge of the EEZ. For the
Southeast Atlantic gillnet fishery
operating in these waters south to 27°51′
N. lat., only gear modification
requirements, similar to final
requirements for anchored gillnets in
Mid/South Atlantic Gillnet Waters, will
be approved in this final rule. For the
Southeastern U.S. Atlantic shark gillnet
fishery operating in these waters south
to 26°46.5′ N. lat., only the following
requirements will be in effect under this
final rule: no net set within 3 nautical
miles (5.6 km) of a right, humpback or
fin whale; and if a right, humpback or
fin whale moves within 3 nautical miles
(5.6 km) of the set gear, the gear is
removed immediately from the water.
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(15) This final rule also incorporates
the modifications to the Southeast U.S.
Restricted Area implemented through a
recent ALWTRP final rule (72 FR 34632,
June 25, 2007). These modifications
include revised management measures
and boundaries for this management
area, as well as associated changes to
the regulations. Consequently, portions
of the Mid/South Atlantic Gillnet
Waters (i.e., waters within 35 nm (64.82
km) of the South Carolina coast) will be
included in the Southeast U.S.
Restricted Area from November 15
through April 15, during the right whale
calving season. Also, based on the
modifications to the June 25, 2007 final
rule (72 FR 34632), NMFS will not be
making the proposed regulatory changes
related to the straight set and strikenet
definitions in this final rule.
Furthermore, this final rule will not add
the straight set definition based on the
deletion of the associated strikenet
definition in the June 25, 2007 final rule
(72 FR 34632).
(16) NMFS proposed definitions in
§ 229.2 for ‘‘sunrise’’ and ‘‘sunset’’;
however, since that time, these
definitions were added through the
Bottlenose Dolphin Take Reduction
Plan (71 FR 24776, April 26, 2006).
Thus, these definitions are not included
in this action.
yshivers on PROD1PC62 with RULES2
Classification
This final rule has been determined to
be significant for the purposes of
Executive Order 12866.
This final rule identifies measures to
reduce the risk of serious injury or
mortality from entanglement of large
whales under the ALWTRP. A DEIS was
prepared for the proposed rule and was
finalized based on the changes made
from the proposed to final rules. NMFS
considered six alternatives for this final
rule; the final preferred alternative is
recognized and justified in the FEIS.
As required by the Regulatory
Flexibility Act, NMFS prepared a Final
Regulatory Flexibility Analysis (FRFA)
for this final rule. The FRFA
incorporates a summary of the
significant issues raised by the public
comments in response to the Initial
Regulatory Flexibility Analysis (IRFA),
and NMFS responses to those comments
provided elsewhere in the preamble to
this final rule, and a summary of the
analyses completed to support the final
action. A copy of this analysis for this
final rule is available from NMFS (see
ADDRESSES). Cost and benefit estimates
were developed and examined for six
regulatory alternatives, including a
status quo (no action alternative). A
summary of the FRFA follows:
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The objective of this final rule, issued
pursuant to section 118 of the Marine
Mammal Protection Act (MMPA), is to
reduce the level of serious injury and
mortality of right, humpback, and fin
whales in commercial east coast trap/
pot and gillnet fisheries. The key
fisheries affected by this final rule
include the American lobster trap/pot
fishery, other trap/pot fisheries, and
gillnetting operations. ALWTRP
requirements could also potentially
affect seafood dealers and processors as
well as fishing gear manufacturers,
suppliers, and marina operators.
However, data are not readily available
on the latter sectors, so the analysis does
not examine them in detail.
There were six alternatives
considered to modify the ALWTRP,
including a status quo (no action
alternative), two preferred alternatives,
and three other alternatives. The final
preferred alternative is a modification to
one of the original preferred
alternatives. All alternatives to the final
rule, except for the status quo (no action
alternative), were evaluated using model
vessels, each of which represents a
group of vessels that share similar
operating characteristics and would face
similar requirements under a given
regulatory alternative. A summary of the
analysis follows:
1. Under Alternative 1, NMFS would
continue with the status quo, i.e., the
baseline set of ALWTRP requirements
currently in place. This would result in
no changes to the current measures
under the ALWTRP and, as such, would
result in no additional economic effects
on the fishing industry. This alternative,
however, would not achieve the
required reduction in incidental
mortality and or serious injury of large
whales in commercial fishing gear, nor
meet the requirements of the ALWTRP,
thus NMFS rejected this alternative.
2. NMFS considered and rejected
Alternative 2, which would implement
broad-based, coast-wide gear
modifications year-round for all Atlantic
fisheries regulated by the ALWTRP.
These gear modifications would
include: The use of weak links on all
flotation devices; discontinuing the
SAM and DAM programs and requiring
the use of entirely sinking and/or
neutrally buoyant groundline effective
12 months after publication of the final
rule; the use of weak links and
anchoring systems for gillnets; and
implementing new gear marking
requirements for buoy lines. This
alternative would also cover several
new fisheries under the ALWTRP
regulations that use gear similar to gear
used by those fisheries already subject
to the regulations, redefine some of the
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regulated area boundaries, extend the
scope of the ALWTRP regulations out to
the eastern edge of the EEZ, and expand
and clarify the areas exempted from the
plan. The incremental costs that
Alternative 2 would impose on the
commercial fishing industry range is
estimated to be approximately $19.2
million per year. NMFS concluded that
the potential for entanglement of whales
in Mid-Atlantic or South Atlantic waters
during summer months is minor, and
that year-round requirements, as
proposed by this alternative, would
offer a marginal risk reduction benefit to
large whales. Seasonal implementation
of gear conversion requirements, instead
of year-round gear modifications, would
also reduce compliance costs for
fishermen without increasing risks to
whales.
3. Alternative 3, which was identified
as one of two preferred alternatives in
the proposed rule, would implement all
of the requirements included in
Alternative 2, except that the
requirements for Mid- and South
Atlantic waters south of 40°00′ N. lat.
would be seasonal rather than yearround. Waters north of 40°00′ N. lat.
would be subject to ALWTRP gear
modifications year-round. The
incremental costs that Alternative 3
would impose on the commercial
fishing industry is similar to costs under
Alternative 2 (approximately $19.2
million per year). NMFS rejected this
alternative as it did not provide
immediate protection to right whales by
offering an expanded SAM zone with
sinking and/or neutrally buoyant
groundline requirements to protect
predictable aggregations of right whales.
4. NMFS considered and rejected
Alternative 4, which consisted of all of
the gear modifications included in
Alternative 2, except that the
requirements for South Atlantic waters
south of the South Carolina/Georgia
border would be seasonal rather than
year-round. Waters north of this border
would be subject to ALWTRP gear
modifications year-round. The
incremental costs that Alternative 4
would impose on the commercial
fishing industry is similar to costs under
Alternative 2 and 3 (approximately
$19.2 million per year). This alternative
was rejected because NMFS concluded
that the potential for entanglement of
whales in Mid-Atlantic waters during
summer months is minor, and that yearround requirements, as proposed by this
alternative, would offer a marginal risk
reduction benefit to large whales.
Seasonal implementation of gear
conversion requirements, instead of
year-round gear modifications, would
also reduce compliance costs for
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fishermen without increasing risks to
whales.
5. NMFS considered and rejected
Alternative 5, which would implement
the requirements included in
Alternative 3, except for the broadbased, coast-wide gear modification
requirements such as the use of entirely
sinking/neutrally buoyant groundline,
expanded weak link requirements for
gillnet gear at night in the Mid-Atlantic,
and weak link and anchoring
requirements for gillnet gear in the
Northeast. Additionally, 6 months after
publication of this final rule, this
alternative would expand the SAM
areas, allow for a second buoy line,
allow both buoy lines to have up to onethird of the bottom portion of the buoy
line to be composed of floating line in
the SAM areas, and discontinue the
DAM program. Alternative 5 would
impose incremental compliance costs of
approximately $1.3 million annually.
The benefits of Alternative 5 for whale
survival are likely to be significantly
lower than the benefits associated with
all other alternatives considered, hence
NMFS did not choose this alternative.
6. NMFS considered and modified
Alternative 6, which was identified as
one of two preferred alternatives in the
proposed rule. Alternative 6 (Draft)
combines elements of Alternative 3 and
Alternative 5. Buoy line weak link
requirements and broad-based gear
requirements (gillnet net panel weak
links, sinking/neutrally buoyant
groundline, anchoring, gear marking,
etc.) would be introduced on the same
schedule and with the same seasonal
and geographic provisions as described
under Alternative 3; however, DAM
requirements would be eliminated six
months after publication of this final
rule, and the expanded SAM zone and
SAM regulations described in
Alternative 5 would apply from six
months after publication until the
broad-based groundline gear
modification are in place, when the
SAM zones would be eliminated. In
response to comments received
regarding economic and operational
concerns resulting from the
implementation of this alternative,
NMFS formulated a final preferred
alternative that builds upon Alternative
6 (Draft). Alternative 6 (Draft) would
impose incremental compliance costs of
approximately $19.2 million annually.
NMFS rejected Alternative 6 (Draft) as it
does not contain modifications that will
allow NMFS to respond to the
comments received while balancing risk
reduction considerations.
7. NMFS selected Alternative 6 (Final
Preferred) in this final rule because it
builds upon Alternative 6 (Draft). This
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alternative will implement all of the
requirements contained in Alternative 3
including the broad-based, coast-wide
gear modifications and seasonal
restrictions. Additionally, as in
Alternative 5, this alternative would
expand the SAM areas, allow for a
second buoy line, allow both buoy lines
to have up to one-third of the bottom
portion of the buoy line to be composed
of floating line in the SAM areas, and
eliminate the DAM program upon
expansion of the SAM areas. The SAM
program will be eliminated when the
broad-based groundline gear
modification becomes effective. Among
all the alternatives considered that
achieve the required reduction in
mortality and serious injury to large
whales in commercial fishing gear, this
final preferred alternative minimizes
potential economic impacts through
various regulatory modifications.
Expanded exemption areas under this
final alternative will lower the number
of vessels affected by regulations, also
reducing socioeconomic impacts of this
final rule itself. Alternative 6 (Final)
would impose estimated incremental
costs of approximately $13.4 million per
year, which is approximately $5.8
million per year less than Alternatives
2, 3, 4, and 6 (Draft). Alternatives 3 and
6 (Draft) were the preferred alternatives
in the proposed rule. This final
preferred alternative will provide an
optional weak link configuration for
gillnet fisheries, which will offer
fishermen the ability to comply in a
low-cost and conservation equivalent
manner. Fishermen will also be able to
pursue lower-cost compliance strategies
through the seasonal restrictions for
both the Mid- and South Atlantic
regions. The risk-reduction tradeoff is
minimal, given that entanglement risk
in the Mid- and South Atlantic is low
in the summer months. NMFS chose
this alternative as it had many of the
components of Alternative 6 (Draft), but
incorporates modifications that will
allow NMFS to respond to comments to
improve the alternative while balancing
risk reduction considerations. For
example, Alternative 6 (Final Preferred)
expands exempted waters off of Maine
and Long Island Sound, based on a
NMFS analysis that, amongst other
reasons, concludes that large whales are
sighted infrequently and do not spend
significant periods of time in these
waters. This change effectively reduces
the number of vessels that must comply
with the ALWTRP gear modification
from 5,118 under the proposed,
preferred Alternatives 3 (Draft) and 6
(Draft) to 4,353 under Alternative 6
(Final Preferred). The gear marking
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57169
requirement of one mark midway along
the buoy line, rather than every ten
fathoms, is more cost effective and
practical based on current technology.
This change effectively reduces the total
number of new gear marks to be
installed by vessels that must comply
with the ALWTRP gear modification
from 2.2 million under the proposed,
preferred Alternatives 3 (Draft) and 6
(Draft) to 0.3 million under Alternative
6 (Final Preferred). This final rule
would also grant an exemption to gillnet
panel weak link and anchoring
requirements to any vessel fishing at
depths greater than 280 fathoms. Whales
are not likely to occur in waters of this
depth. Additionally, allowing anchored
gillnet vessels under Alternative 6
(Final Preferred) to use an alternate
weak link configuration that is the
functional equivalent of what was
proposed enables fishermen to have
more options and flexibility when
configuring their gear. These and other
variations to the Final Preferred
Alternative (6) decrease the number of
affected vessels and result in reductions
in compliance costs, while sacrificing
little in terms of entanglement risk
reduction.
NMFS solicited public comments on
both the Draft Environmental Impact
Statement (DEIS) (70 FR 9306, February
25, 2005; 70 FR 15315, March 25, 2005)
and proposed rule (70 FR 35894, June
21, 2005; 70 FR 40301, July 13, 2005)
through several different means
including written comment. The public
also had the opportunity to provide oral
comments at 13 public hearings held in
the states of Maine, Massachusetts,
Rhode Island, New Jersey, Maryland,
Virginia, North Carolina, and Florida. A
summary of all comments received and
NMFS’ responses is included in Volume
II of the FEIS. Significant issues were
raised by the public in response to the
expected impacts of this final rule. In
general, areas of concern included: (1)
The implementation time for sinking
and/or neutrally buoyant groundline
requirements, as well as other new
regulations under this final rule; (2) the
delineation of exemption areas; (3) the
practicality of the proposed gear
marking scheme; (4) the configuration of
gillnet weak links; (5) the specification
of areas and times during which
ALWTRP requirements would be in
effect; and (6) the implementation of
gillnet anchoring requirements,
especially in waters within 300 yards
(900 ft or 274.3 m) of the shoreline.
NMFS formulated the final preferred
alternative based on these public
comments and additional information
received. This final alternative
introduces a number of significant
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changes, including: (1) Expanding
exempted waters off of Maine and Long
Island Sound; (2) allowing anchored
gillnet vessels to use an alternate weak
link configuration; and (3) allowing
anchored gillnet vessels operating
within 300 yards (900 ft or 274.3 m) of
the shoreline of North Carolina to use an
alternate anchoring configuration. These
and other minor variations decrease the
number of affected vessels and result in
reductions in compliance costs, while
sacrificing little in terms of
entanglement risk reduction.
The small entities affected by this
final rule are commercial trap/pot and
gillnet fisherman operating in Northeast
Atlantic, Mid-Atlantic, and Southeast
Atlantic waters. The analysis of the final
preferred alternative identified
approximately 4,350 vessels that would
be affected by this final rule (this
number does not include Southeastern
U.S. Atlantic shark gillnet vessels, as the
analysis for this action concluded that
these vessels would not incur
significant compliance costs).
In the lobster trap/pot fishery,
approximately 2,900 vessels would be
affected. The analysis identified 11
vessel segments that can be considered
‘‘heavily affected’’, where estimated
compliance costs exceeded 15 percent
of average annual revenues. Nearly all of
these segments are composed of smaller
(Class I or Class II) vessels, which
typically have a smaller revenue base
with which to absorb compliance costs.
Seven of these segments represent
lobster/trap vessels.
Approximately 1,980 other vessels fell
into the ‘‘at-risk vessel’’ category, where
estimated compliance costs were
between 5 and 15 percent of average
annual revenues. The majority of at-risk
vessels are Class II lobster vessels; of
these, the most affected subsets are
vessels in Maine, which are estimated to
have greater gear loss costs. A variety of
other vessels fall in the at-risk range,
including northern nearshore lobster
vessels, several categories of other trap/
pot vessels (e.g., black sea bass, hagfish,
red crab), and Class I gillnet vessels in
the Mid-Atlantic.
This final rule contains collection of
information requirements subject to the
Paperwork Reduction Act (PRA),
because of the proposed gear marking
scheme. The proposed collection of
information requirement was submitted
to the Office of Management and Budget
(OMB) for approval, and is still under
review. Once the information collection
has been approved, NMFS will publish
a Federal Register notice providing the
OMB approval control number. Public
comment was sought regarding whether
this proposed collection of information
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is necessary for the proper performance
and function of the agency, including:
The practical utility of the information;
the accuracy of the burden estimate; the
opportunities to enhance the quality,
utility, and clarity of the information to
be collected; and the ways to minimize
the burden of the collection of
information, including the use of
automated collection techniques or
other forms of information technology.
Send comments regarding this burden
estimate, or any other aspect of this data
collection, including suggestions for
reducing the burden, to NMFS (see
ADDRESSES) and by e-mail to
David_Rostker@omb.eop.gov, or fax to
202–395–7285.
This collection of information
requirement applies to a total of 2,695
newly affected vessels, including 64
model vessel types. Model vessel types
were developed for gillnet fisheries,
lobster trap/pot fisheries, and other
trap/pot fisheries. Total burden hours
for all newly affected vessels is 40,702
over three years or 13,567 per year.
Total cost burden for all newly affected
vessels is $26,863 over three years or
$8,954 per year. For more information,
please see the PRA submission
associated with this rulemaking.
Any information collection
requirements subject to PRA and related
to VMS requirements in the U.S.
Southeast Atlantic shark gillnet fishery
were addressed in a previous
rulemaking (69 FR 51010, August 17,
2004) and approved by OMB under
control number 0648–0372. Fishermen
will not incur any additional costs as
they currently have all the equipment
required to comply with the reporting
requirements.
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 PRA, unless
that collection of information displays a
currently valid OMB Control Number.
NMFS has determined that this final
action is consistent to the maximum
extent practicable with the approved
coastal management program of the U.S.
Atlantic coastal states. The proposed
rule, RIR, RFA analysis, and DEIS were
submitted to the responsible state
agencies for review under section 307 of
the Coastal Zone Management Act
(CZMA). The following states agreed
with NMFS’ determination: New
Hampshire, Rhode Island, New Jersey,
Pennsylvania, Delaware, Virginia, South
Carolina, Georgia, and Florida. Maine,
Massachusetts, and Maryland did not
respond, therefore, consistency is
inferred. Three states, Connecticut, New
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York, and North Carolina conditionally
concurred with NMFS’ conclusion that
the proposed action is consistent with
the enforceable policies of the approved
coastal management program for that
state; however, the North Carolina
conditional concurrence was treated as
an objection because NMFS could not
meet the state agency’s conditions.
The Connecticut Department of
Environmental Protection and New
York State Department of
Environmental Conservation concurred
with NMFS’ determination that the
amendments to the ALWTRP are
consistent to the maximum extent
practicable with the enforceable policies
of the states’ Coastal Management
Programs provided that NMFS adopt the
modifications recommended by the
Connecticut Marine Fisheries Division.
The recommended modifications
included an adjustment of the proposed
ALWTRP exempted line for Long Island
Sound. Without this adjustment, the
Connecticut Department of
Environmental Protection indicated that
the proposed action would create an
unjustified economic hardship on the
Connecticut fishing industry, as there is
an absence of whale interactions in this
area. This final rule adopts the
modifications suggested by the
Connecticut Marine Fisheries Division
and New York State Department of
Environmental Conservation; therefore,
in accordance with 15 CFR 930.4(a)(2),
the final rule was modified pursuant to
the state agency’s conditions that allow
the state agency to concur with the
Federal action.
The NCDCM also conditionally
concurred with NMFS’ determination
that the proposed action is consistent to
the maximum extent practicable with
the enforceable policies of North
Carolina’s coastal management program.
NCDCM was concerned that the
proposed action would adversely affect
the public’s ability to conduct
recreational and/or commercial fishing,
causing safety hazards as well as
economic and operational burdens.
Thus, NCDCM offered three conditions
that the agency would have to adopt in
order to be consistent with North
Carolina’s coastal management program.
First, NCDCM recommended that the
mid-Atlantic gillnet restriction season
from December 1 through March 31 of
any year should not be expanded to the
proposed period of September 1 through
May 31. Alternatively, NCDCM
suggested that, if the season is
expanded, the inshore small mesh
gillnet fishery (<5 inches (0.1 m), 300yard (274.3 m or 900 ft) maximum set)
be allowed to use deadweight anchors
on the inshore end of the net and
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Danforth-style anchors with a minimum
weight of 8 lb on the offshore end.
Second, NCDCM required that the
proposal to implement the mandatory
use of sinking and/or neutrally buoyant
groundline on pots/traps be replaced
with an alternative for reducing the
profile of the groundline, such as
weaving sections of lead core line in the
groundlines currently in use.
Third, in order to be found consistent
with North Carolina’s coastal
management program, NCDCM required
that the gear marking requirement of the
ALWTRP be consistent with those
already implemented by other protected
species take reduction plans and/or
Regional Fishery Management Council
or NMFS FMPs for oceanic waters.
This final rule adopts an optional
anchoring requirement, and also
considers gear marking requirements by
other take reduction or fishery
management plans as suggested by
NCDCM. However, this final rule does
not allow for a low profile groundline
option. Thus, NMFS did not meet all the
state agency’s conditions. Therefore,
pursuant to 15 CFR 930.4, the
requirements of paragraphs (a)(1)
through (3) were not met, and the
NCDCM no longer concurs with the
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15:40 Oct 04, 2007
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determination that the proposed
measures are consistent to the
maximum extent practicable with North
Carolina’s Coastal Management
Program.
This final rule contains policies with
federalism implications as that term is
defined in Executive Order 13132.
Accordingly, the Assistant Secretary for
Legislative and Intergovernmental
Affairs at the Department of Commerce
provided notice of the DEIS and
proposed rule to the appropriate
official(s) of affected state, local, and/or
tribal governments. Two letters were
sent to officials in Maine, New
Hampshire, Massachusetts, Rhode
Island, Connecticut, New York, New
Jersey, Pennsylvania, Maryland,
Virginia, Delaware, North Carolina,
South Carolina, Georgia, and Florida,
requesting a review of the DEIS and
proposed rule as the proposed
amendments could have a direct impact
on the State. The purpose of these
proposed amendments and their
components were outlined, and a
justification for the proposed rule was
provided to each state through these
letters. No concerns were raised by the
states contacted; hence, NMFS will infer
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57171
that these states concur with the finding
that the proposed regulations for
amending the ALWTRP were consistent
with fundamental federalism principles
and federalism policymaking criteria.
An informal consultation under the
ESA for this final rule to modify the
ALWTRP was concluded on December
21, 2004. As a result of the informal
consultation, the Regional
Administrator determined that the
measures to modify the ALWTRP are
not likely to adversely affect ESA-listed
cetaceans, sea turtles, fish, or critical
habitat that occur within the area
affected by the rulemaking.
Modifications are being made to the
ALWTRP to more broadly address the
incidental entanglement of large whales
in fishing gear that result in serious
injury and mortality. Some of these
modifications (e.g., regulating additional
trap/pot and gillnet fisheries under the
ALWTRP, requiring the broad-based use
of sinking and/or neutrally buoyant
groundline) are expected to have an
effect on ESA-listed species. However,
depending on the species, all of the
effects are expected to be either
beneficial or negligible.
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References
Baumgartner, M.F. and B.R. Mate. 2005.
Summer and fall habitat of North Atlantic
right whales (Eubalaena glacialis) inferred
from satellite telemetry, Canadian Journal of
Aquatic Science, 62: 527–543.
Clapham, P.J. and R.M. Pace, III. 2001.
Defining triggers for temporary area closures
to protect right whales from entanglements:
issues and options. Northeast Fisheries
Science Center Reference Document 01–06.
April 2001.
Cole, T., D. Hartley, and M. Garron. 2006.
Mortality and Serious Injury Determinations
for Baleen Whale Stocks along the Eastern
Seaboard of the United States, 2000–2004.
Northeast Fisheries Science Center Reference
Document 06–04. pp. 26.
DeAlteris, J., A. Fridman, D. Williams, and
J. Guimond. 2002. Estimation of the Tractive
Force of the Northern Right Whale
(Eubalaena glacialis). Revised final report
submitted to the National Marine Fisheries
Service, Northeast Region Protected
Resources Division, Gear Research Team.
Johnson, A.J., G.S. Salvador, J.F. Kenney, J.
Robbins, S.D. Kraus, S.C. Landry, and P.J.
VerDate Aug<31>2005
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Clapham. 2005. Fishing gear involved in
entanglements of right and humpback
whales, Marine Mammal Science, 21(4): 635–
645.
Keller, C.A., L.I. Ward-Geiger, W.B. Brooks,
C.K. Slay, C.R. Taylor, and B.J. Zoodsma.
2006. North Atlantic Right Whale
Distribution in Relation to Sea-Surface
Temperature in the Southeastern United
States Calving Grounds. Marine Mammal
Science, 22(2): 426–445.
Mate, B.R.; Nieukirk, S.L.; and S.D. Kraus.
1997. Satellite-monitored movements of the
northern right whale, Journal of Wildlife
Management, 61(4).
Merrick, R.L. 2005. Seasonal management
areas to reduce ship strikes of northern right
whales in the Gulf of Maine. U.S. Department
of Commerce, Northeast Fisheries Science
Center Reference Document 05–19; 18 pp.
NMFS. 2002. Large Whale Gear Research
Summary. Prepared by the Gear Research
Team, National Marine Fisheries Service,
Northeast Regional Office.
NMFS. 2004. Draft Environmental Impact
Statement on the Proposed Rule to Amend
the Atlantic Large Whale Take Reduction
Plan. Northeast Region.
PO 00000
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RFMRP. 2005. Marine mammal abundance
survey for North Atlantic right whales in the
New York Bight and the Mid Atlantic region.
Riverhead Foundation for Marine Research
and Preservation. Draft report to the National
Fish and Wildlife Foundation. 28 pp.
Waring, G.T., E. Josephson, C.P. Fairfield,
and K. Maze-Foley (eds.), U.S. Atlantic and
Gulf of Mexico marine mammal stock
assessments—2005, NOAA Technical
Memorandum NOAA–NE–194, 2006.
List of Subjects
50 CFR Part 229
Administrative practice and
procedure, Confidential business
information, Fisheries, Marine
mammals, Reporting and recordkeeping
requirements.
50 CFR Part 635
Fisheries, Fishing, Fishing vessels,
Foreign relations, Imports, Penalties,
Reporting and recordkeeping
requirements, Treaties.
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BILLING CODE 3510–22–C
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Federal Register / Vol. 72, No. 193 / Friday, October 5, 2007 / Rules and Regulations
50 CFR Part 648
Fisheries, Fishing, Reporting and
recordkeeping requirements.
Dated: September 21, 2007.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
For the reasons set out in the
preamble, 50 CFR parts 229, 635, and
648 are amended to read as follows:
I
PART 229—AUTHORIZATION FOR
COMMERCIAL FISHERIES UNDER THE
MARINE MAMMAL PROTECTION ACT
OF 1972
1. The authority citation for 50 CFR
part 229 continues to read as follows:
I
Authority: 16 U.S.C. 1361 et seq.;
§ 229.32(f) also issued under 16 U.S.C. 1531
et seq.
2. In § 229.2, the definitions of
‘‘Lobster trap’’ and ‘‘Lobster trap trawl’’
are removed. The definitions of
‘‘Anchored gillnet’’, ‘‘Gillnet’’,
‘‘Groundline’’, ‘‘Neutrally buoyant
line’’, ‘‘Sinking line’’, and ‘‘Stowed’’ are
revised in alphabetical order to read as
follows below. The definitions of ‘‘Bitter
end’’, ‘‘Bottom portion of the line’’, ‘‘Tie
loops’’, ‘‘Trap/Pot’’, ‘‘Trap/pot trawl’’,
and ‘‘Up and down line’’ are added in
alphabetical order to read as follows:
I
§ 229.2
Definitions.
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*
*
*
*
*
Anchored gillnet means any gillnet
gear, including an anchored float gillnet,
sink gillnet or stab net, that is set
anywhere in the water column and
which is anchored, secured, or weighted
to the bottom of the sea. Also called a
set gillnet.
*
*
*
*
*
Bitter end means the end of a line that
detaches from a weak link.
Bottom portion of the line means, for
buoy lines, the portion of the line in the
water column that is closest to the
fishing gear.
*
*
*
*
*
Gillnet means fishing gear consisting
of a wall of webbing (meshes) or nets,
designed or configured so that the
webbing (meshes) or nets are placed in
the water column, usually held
approximately vertically, and are
designed to capture fish by
entanglement, gilling, or wedging. The
term ‘‘gillnet’’ includes gillnets of all
types, including but not limited to sink
gillnets, other anchored gillnets (e.g.,
anchored float gillnets, stab, and set
nets), and drift gillnets. Gillnets may or
may not be attached to a vessel.
Groundline, with reference to trap/pot
gear, means a line connecting traps in a
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trap trawl, and, with reference to gillnet
gear, means a line connecting a gillnet
or gillnet bridle to an anchor or buoy
line.
*
*
*
*
*
Neutrally buoyant line means, for
both groundlines and buoy lines, line
that has a specific gravity greater than
or equal to 1.030, and, for groundlines
only, does not float at any point in the
water column (See also Sinking line).
*
*
*
*
*
Sinking line means, for both
groundlines and buoy lines, line that
has a specific gravity greater than or
equal to 1.030, and, for groundlines
only, does not float at any point in the
water column (See also Neutrally
buoyant line).
*
*
*
*
*
Stowed means traps/pots and gillnets
that are unavailable for immediate use
and further, all gillnets are stored in
accordance with the following:
(1) All nets are covered with canvas
or other similar material and lashed or
otherwise securely fastened to the deck,
rail, or drum, and all buoys larger than
6 inches (15.24 cm) in diameter, high
flyers, and anchors are disconnected;
and
(2) Any other method of stowage
authorized in writing by the Regional
Administrator and subsequently
published in the Federal Register.
*
*
*
*
*
Tie loops means the loops on a gillnet
panel used to connect net panels to the
buoy line, groundline, bridle or each
other.
Trap/Pot means any structure or other
device, other than a net or longline, that
is placed, or designed to be placed, on
the ocean bottom and is designed for or
is capable of, catching species including
but not limited to lobster, crab (red,
Jonah, rock, and blue), hagfish, finfish
(black sea bass, scup, tautog, cod,
haddock, pollock, redfish (ocean perch),
and white hake), conch/whelk, and
shrimp.
Trap/pot trawl means two or more
trap/pots attached to a single
groundline.
Up and down line means the line that
connects the float-line and lead-line at
the end of each gillnet net panel.
*
*
*
*
*
I 3. In § 229.3:
I a. Redesignate paragraphs (l), (m), (n),
(o), (p), (q), and (r) as paragraphs (m),
(n), (o), (p), (q), (r), and (s), respectively;
and
I b. Paragraphs (h) through (k) are then
revised and paragraph (l) is added to
read as follows:
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§ 229.3
Prohibitions.
*
*
*
*
*
(h) It is prohibited to fish with or
possess trap/pot gear in the areas and
during the times specified in § 229.32
(c)(2) through (c)(9) unless the trap/pot
gear complies with the marking
requirements, closures, modifications,
and restrictions specified in
§ 229.32(b)(2)(ii), (b)(2)(iii), and (c)(1)
through (c)(9), or unless the gear is
stowed as specified in § 229.2.
(i) It is prohibited to fish with or
possess anchored gillnet gear in the
areas and during the times specified in
§ 229.32(d)(2) through (d)(7) unless that
gillnet gear complies with the marking
requirements, closures, modifications,
and restrictions specified in
§ 229.32(b)(2)(ii), (b)(2)(iii), and (d)(1)
through (d)(7), or unless the gear is
stowed as specified in § 229.2.
(j) It is prohibited to fish with or
possess drift gillnet gear in the areas and
during the times specified in
§ 229.32(e)(1) through (e)(6) unless the
drift gillnet gear complies with the
marking requirements, closures,
modifications, and restrictions specified
in § 229.32(b)(2)(ii), (b)(2)(iii), and (e)(1)
through (e)(6), or unless the gear is
stowed as specified in § 229.2.
(k) It is prohibited to fish with or
possess gillnet gear in the areas and
during the times specified in
§ 229.32(f)(1) and (g)(1) unless the
gillnet gear complies with the marking
requirements, closures, modifications,
and restrictions specified in
§ 229.32(b)(2)(ii), (b)(2)(iii), (f)(2)(ii),
(f)(2)(iv), (f)(2)(v), and (g)(3), or for (g)(3)
unless the gear is stowed as specified in
§ 229.2.
(l) It is prohibited to fish with or
possess shark gillnet gear (i.e. gillnet
gear for shark with webbing of 5 inches
(12.7 cm) or greater stretched mesh) in
the areas and during the times specified
in § 229.32(f)(1), (g)(1) and (h)(1) unless
the gear complies with the marking
requirements, closures, modifications,
and restrictions specified in
§ 229.32(b)(2)(i), (b)(2)(iii), (f)(2)(ii),
(f)(2)(iii), (f)(2)(v), (g)(2), and (h)(2), or
for the gear marking requirements for
(h)(2) unless the gear is stowed as
specified in § 229.2.
*
*
*
*
*
I 4. Section § 229.32 is amended as
follows:
I A. Paragraphs (f) introductory text,
(f)(2), and (f)(3) are revised effective
November 5, 2007.
I B. Amendments to § 229.32 (f)(1)(iii)
and (g)(4)(i)(B)(1)(vi) are added effective
November 5, 2007 to April 5, 2008.
I C. Paragraphs (f)(1)(ii) and
(g)(4)(i)(B)(1)(iii) are removed and
reserved effective November 5, 2007.
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§ 229.32 Atlantic large whale take
reduction plan regulations.
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*
*
*
*
*
(f) Restrictions applicable to the
Southeast U.S. Restricted Area and the
Southeast U.S. Monitoring Area—
(1) * * *
(i) * * *
(iii) Southeast U.S. Monitoring Area—
(A) Management areas and restricted
periods. From December 1 through
March 31, the Southeast U.S.
Monitoring Area consists of the area
from 27°51′ N. lat. south to 26°46.50′ N.
lat. (near West Palm Beach, FL),
extending from the shoreline or
exemption line out to 80°00′ W. long.,
unless the Assistant Administrator
changes that area in accordance with
paragraph (g) of this section.
(B) Vessel monitoring systems and
observer requirements. No person may
fish for shark with gillnet with webbing
of 5 inches (12.7 cm) or greater stretched
mesh in the Southeast U.S. Monitoring
Area during the restricted period unless
the person or vessel satisfies the vessel
monitoring system and observer
requirements listed below.
(1) Vessel monitoring systems. No
person or vessel may fish with or
possess gillnet gear for shark with
webbing of 5 inches (12.7 cm) or greater
stretched mesh in the Southeast U.S.
Monitoring Area during the restricted
period unless the operator of the vessel
is in compliance with the vessel
monitoring system (VMS) requirements
found in 50 CFR 635.69.
(2) At-sea observer coverage. NMFS
may select any shark gillnet vessel (i.e.,
vessel fishing gillnet gear for shark with
webbing of 5 inches (12.7 cm) or greater
stretched mesh) regulated under
§ 229.32 to carry an observer. When
selected, vessels are required to take
observers on a mandatory basis in
compliance with the requirements for
at-sea observer coverage found in 50
CFR 229.7. Any vessel that fails to carry
an observer once selected is prohibited
from fishing pursuant to 50 CFR part
635.
(2) Gear marking requirements. From
November 15 through March 31 of the
following year, no person may fish with
gillnet gear in the Southeast U.S.
Restricted Area and Southeast U.S.
Monitoring Area unless that gear is
marked according to the gear marking
code specified under paragraph (b) of
this section. All buoy lines must be
marked within 2 ft (0.6m) of the top of
the buoy line and midway along the
length of the buoy line. From November
15, 1999, each net panel must be
marked along both the float line and the
lead line at least once every 100 yards
(92.4m).
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(3) Observer requirement. No person
may fish for shark with gillnet with
webbing of 5 inches (12.7cm) or greater
stretched mesh in the Southeast U.S.
Restricted Area from December 1
through March 31 south of 29°00′ N. lat.
unless the operator of the vessel calls
the Southeast Fisheries Science Center
Panama City Laboratory in Panama City,
FL, not less than 48 hours prior to
departing on any fishing trip, in order
to arrange for observer coverage. If the
Panama City Laboratory requests that an
observer be taken on board a vessel
during a fishing trip at any time from
December 1 through March 31 south of
29° 00′ N. lat., no person may fish with
such gillnet gear aboard that vessel in
the Southeast U.S. Restricted Area
unless an observer is on board that
vessel during the trip.
*
*
*
*
*
(g) * * *
(4) * * *
(i) * * *
(B) * * *
(1) * * *
(vi) Net panel weak links. The
breaking strength of each weak link
must not exceed 1,100 lb (499.0 kg). The
weak link requirements apply to all
variations in panel size. One weak link
must be placed in the center of the
floatline and one weak link must be
placed in the center of each of the up
and down lines at both ends of the net
panel. Additionally, one weak link must
be placed as close as possible to each
end of the net panels on the floatline; or
one weak link must be placed between
floatline tie-loops between net panels
and one weak link must be placed
where the floatline tie-loops attach to
the bridle, buoy line, or groundline at
each end of a net string.
*
*
*
*
*
I 5. Revise § 229.32, effective April 5,
2008 except for paragraphs (c)(5)(ii)(B),
(c)(6)(ii)(B), (c)(7)(ii)(C), (c)(8)(ii)(B),
(c)(9)(ii)(B), (d)(6)(ii)(D), and
(d)(7)(ii)(D), which will be effective
October 5, 2008, to read as follows:
§ 229.32 Atlantic large whale take
reduction plan regulations.
(a)(1) Purpose and scope. The purpose
of this section is to implement the
Atlantic Large Whale Take Reduction
Plan to reduce incidental mortality and
serious injury of fin, humpback, and
right whales in specific Category I and
Category II commercial fisheries from
Maine through Florida. The measures
identified in the Atlantic Large Whale
Take Reduction Plan are also intended
to benefit minke whales, which are not
designated as a strategic stock, but are
known to be taken incidentally in
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57181
gillnet and trap/pot fisheries. The gear
types affected by this plan include
gillnets (e.g., anchored, drift, and shark)
and traps/pots.
(2) Regulated waters. The regulations
in this section apply to all U.S. waters
in the Atlantic except for the areas
exempted in paragraph (a)(3) of this
section.
(3) Exempted waters. (i) The
regulations in this section do not apply
to waters landward of the first bridge
over any embayment, harbor, or inlet in
Massachusetts.
(ii) The regulations in this section do
not apply to waters landward of the 72
COLREGS demarcation lines
(International Regulations for
Preventing Collisions at Sea, 1972), as
depicted or noted on nautical charts
published by the National Oceanic and
Atmospheric Administration (Coast
Charts 1:80,000 scale), and as described
in 33 CFR part 80 with the exception of
the COLREGS lines for Casco Bay
(Maine), Portsmouth Harbor (New
Hampshire), Gardiners Bay and Long
Island Sound (New York), and the state
of Massachusetts.
(iii) Other exempted waters. The
regulations in this section do not apply
to waters landward of the following
lines:
Maine
A line connecting the following
points (Quoddy Narrows/U.S.-Canada
border to Odiornes Pt., Portsmouth,
New Hampshire):
44°49.67′ N. lat., 66°57.77′ W. long. (R
N ‘‘2’’, Quoddy Narrows)
44°48.64′ N. lat., 66°56.43′ W. long. (G
‘‘1’’ Whistle, West Quoddy Head)
44°47.36′ N. lat., 66°59.25′ W. long. (R
N ‘‘2’’, Morton Ledge)
44°45.51′ N. lat., 67°02.87′ W. long. (R
‘‘28M’’ Whistle, Baileys Mistake)
44°37.70′ N. lat., 67°09.75′ W. long.
(Obstruction, Southeast of Cutler)
44°27.77′ N. lat., 67°32.86′ W. long.
(Freeman Rock, East of Great Wass
Island)
44°25.74′ N. lat., 67°38.39′ W. long. (R
‘‘2SR’’ Bell, Seahorse Rock, West of
Great Wass Island)
44°21.66′ N. lat., 67°51.78′’ W. long. (R
N ‘‘2’’, Petit Manan Island)
44°19.08′ N. lat., 68°02.05′ W. long. (R
‘‘2S’’ Bell, Schoodic Island)
44°13.55′ N. lat., 68°10.71′ W. long. (R
‘‘8BI’’ Whistle, Baker Island)
44°08.36′ N. lat., 68°14.75′ W. long.
(Southern Point, Great Duck Island)
43°59.36′ N. lat., 68°37.95′ W. long. (R
‘‘2’’ Bell, Roaring Bull Ledge, Isle Au
Haut)
43°59.83′ N. lat., 68°50.06′’ W. long. (R
‘‘2A’’ Bell, Old Horse Ledge)
43°56.72′ N. lat., 69°04.89′ W. long. (G
‘‘5TB’’ Bell, Two Bush Channel)
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43°50.28′ N. lat., 69°18.86′ W. long. (R
‘‘2 OM’’ Whistle, Old Man Ledge)
43°48.96′ N. lat., 69°31.15′ W. long. (GR
C ‘‘PL’’, Pemaquid Ledge)
43°43.64′ N. lat., 69°37.58′ W. long. (R
‘‘2BR’’ Bell, Bantam Rock)
43°41.44′ N. lat., 69°45.27′ W. long. (R
‘‘20ML’’ Bell, Mile Ledge)
43°36.04′ N. lat., 70°03.98′ W. long. (RG
N ‘‘BS’’, Bulwark Shoal)
43°31.94′ N. lat., 70°08.68′ W. long. (G
‘‘1’’, East Hue and Cry)
43°27.63′ N. lat., 70°17.48′ W. long. (RW
‘‘WI’’ Whistle, Wood Island)
43°20.23′ N. lat., 70°23.64′ W. long. (RW
‘‘CP’’ Whistle, Cape Porpoise)
43°04.06′ N. lat., 70°36.70′ W. long. (R
N ‘‘2MR’’, Murray Rock)
43°02.93′ N. lat., 70°41.47′ W. long. (R
‘‘2KR’’ Whistle, Kittery Point)
43°02.55′ N. lat., 70°43.33′ W. long.
(Odiornes Pt., Portsmouth, New
Hampshire)
New Hampshire
A line from 42°53.691′ N. lat.,
70°48.516′ W. long. to 42°53.516′ N.
lat., 70°48.748′ W. long. (Hampton
Harbor)
A line from 42°59.986′ N. lat.,
70°44.654′ W. long. to 42°59.956′ N.,
70°44.737′ W. long. (Rye Harbor)
Rhode Island
A line from 41°22.441′ N. lat.,
71°30.781′ W. long. to 41°22.447′ N.
lat., 71°30.893′ W. long. (Pt. Judith
Pond Inlet)
A line from 41°21.310′ N. lat.,
71°38.300′ W. long. to 41°21.300′ N.
lat., 71°38.330′ W. long. (Ninigret
Pond Inlet)
A line from 41°19.875′ N. lat.,
71°43.061′ W. long. to 41°19.879′ N.
lat., 71°43.115′ W. long.
(Quonochontaug Pond Inlet)
A line from 41°19.660′ N. lat.,
71°45.750′ W. long. to 41°19.660′ N.
lat., 71°45.780′ W. long. (Weekapaug
Pond Inlet)
New York
A line that follows the territorial sea
baseline through Block Island Sound
(Watch Hill Point, RI, to Montauk
Point, NY)
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South Carolina
A line from 32°34.717′ N. lat.,
80°08.565′ W. long. to 32°34.686′ N.
lat., 80°08.642′ W. long. (Captain
Sams Inlet)
(4) Sinking and/or neutrally buoyant
groundline exemption. The fisheries
regulated under this section are exempt
from the requirement to have
groundlines composed of sinking and/or
neutrally buoyant line if their
groundline is at a depth equal to or
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15:40 Oct 04, 2007
Jkt 214001
greater than 280 fathoms (1,680 ft or
512.1 m) (as shown on NOAA charts
13200 (Georges Bank and Nantucket
Shoals, 1:400,000), 12300 (NY
Approaches—Nantucket Shoals to Five
Fathom Bank, 1:400,000), 12200 (Cape
May to Cape Hatteras, 1:419,706), 11520
(Cape Hatteras to Charleston, 1:432,720),
11480 (Charleston Light to Cape
Canaveral, 1:449,659) and 11460(Cape
Canaveral to Key West, 1:466,940)).
(5) Net panel weak link and anchoring
exemption. The anchored gillnet
fisheries regulated under this section are
exempt from the requirement to install
weak links in the net panel and anchor
each end of the net string if the float-line
is at a depth equal to or greater than 280
fathoms (1,680 ft or 512.1 m) (as shown
on NOAA charts 13200 (Georges Bank
and Nantucket Shoals, 1:400,000),
12300 (NY Approaches—Nantucket
Shoals to Five Fathom Bank, 1:400,000),
12200 (Cape May to Cape Hatteras,
1:419,706), 11520 (Cape Hatteras to
Charleston, 1:432,720), 11480
(Charleston Light to Cape Canaveral,
1:449,659) and 11460(Cape Canaveral to
Key West, 1:466,940)).
(b) Gear marking requirements. (1)
Specified gear consists of trap/pot gear
and gillnet gear set in specified areas.
(2) Specified areas. The following
areas are specified for gear marking
purposes: Northern Inshore State Trap/
Pot Waters, Cape Cod Bay Restricted
Area, Stellwagen Bank/Jeffreys Ledge
Restricted Area, Northern Nearshore
Trap/Pot Waters Area, Great South
Channel Restricted Trap/Pot Area, Great
South Channel Restricted Gillnet Area,
Great South Channel Sliver Restricted
Area, Southern Nearshore Trap/Pot
Waters Area, Offshore Trap/Pot Waters
Area, Other Northeast Gillnet Waters
Area, Mid/South Atlantic Gillnet Waters
Area, Other Southeast Gillnet Waters
Area, Southeast U.S. Restricted Area,
and Southeast U.S. Monitoring Area.
(i) Requirements for Shark Gillnet
Gear in the Southeast U.S. Restricted
Area S, Southeast U.S. Monitoring Area
and Other Southeast Gillnet Waters—
(A) Color code. Shark gillnet gear (i.e.,
gillnet gear for shark with webbing of 5
inches (12.7 cm) or greater stretched
mesh) in the Southeast U.S. Restricted
Area S, Southeast U.S. Monitoring Area,
and Other Southeast Gillnet Waters
must be marked with the appropriate
color code to designate gear types and
areas as follows:
(1) Gear type code. Shark gillnet gear
must be marked with a green marking.
(2) Area code. Shark gillnet gear set in
the Southeast U.S. Restricted Area S,
Southeast U.S. Monitoring Area, and
Other Southeast Gillnet Waters must be
marked with a blue marking.
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(B) Markings. All specified gear in
specified areas must be marked with
two color codes, one designating the
gear type, the other indicating the area
where the gear is set. Each color of the
two-color code must be permanently
marked on or along the line or lines
specified below under paragraphs
(b)(2)(i)(C) and (D) of this section. Each
color mark of the color codes must be
clearly visible when the gear is hauled
or removed from the water. Each mark
must be at least 4 inches (10.2 cm) long.
The two color marks must be placed
within 6 inches (15.2 cm) of each other.
If the color of the rope is the same as
or similar to a color code, a white mark
may be substituted for that color code.
In marking or affixing the color code,
the line may be dyed, painted, or
marked with thin colored whipping
line, thin colored plastic, or heat-shrink
tubing, or other material; or a thin line
may be woven into or through the line;
or the line may be marked as approved
in writing by the Assistant
Administrator. A brochure illustrating
the techniques for marking gear is
available from the Regional
Administrator, NMFS, Northeast Region
upon request.
(C) Buoy line markings. All buoy lines
greater than 4 feet (1.22 m) long must be
marked within 2 feet (0.6 m) of the top
of the buoy line (closest to the surface)
and midway along the length of the
buoy line.
(D) Net panel markings. Each gillnet
net panel must be marked along both
the floatline and the leadline at least
once every 100 yards (91.4 m), unless
otherwise required by the Assistant
Administrator under paragraph (i) of
this section.
(ii) Requirements for other specified
areas. Any person who owns or fishes
with specified gear in the other
specified areas must mark that gear in
accordance with paragraphs (b)(2)(ii)(A),
(b)(2)(ii)(B), and (b)(2)(iii) of this
section, unless otherwise required by
the Assistant Administrator under
paragraph (i) of this section.
(A) Color code. Specified gear must be
marked with the appropriate colors to
designate gear-types and areas as
follows:
(1) Trap/pot gear in the Northern
Inshore State Trap/Pot Waters Area, the
Cape Cod Bay Restricted Area, the
Stellwagen Bank/Jeffreys Ledge
Restricted Area, the Great South
Channel Restricted Trap/Pot Area where
it overlaps with Lobster Management
Area (LMA) 2 and the Outer Cape LMA
(as defined in the American Lobster
Fishery regulations in 50 CFR 697.18),
and the Northern Nearshore Trap/Pot
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Waters Area must be marked with a red
marking.
(2) Trap/pot gear in the Southern
Nearshore Trap/Pot Waters Area must
be marked with an orange marking.
(3) Trap/pot gear in the Great South
Channel Restricted Trap/Pot Area where
it overlaps with LMA 2⁄3 Overlap and
LMA 3 (as defined in the American
Lobster Fishery regulations in 50 CFR
697.18), and the Offshore Trap/Pot
Waters Area must be marked with a
black marking.
(4) Anchored and drift gillnet gear in
the Cape Cod Bay Restricted Area,
Stellwagen Bank/Jeffreys Ledge
Restricted Area, Great South Channel
Restricted Gillnet Area, Great South
Channel Sliver Restricted Area, and
Other Northeast Gillnet Waters Area
must be marked with a green marking.
(5) Anchored and drift gillnet gear in
the Mid/South Atlantic Gillnet Waters
Area must be marked with a blue
marking.
(6) Gillnet gear (except gillnet gear for
shark with webbing of 5 inches (12.7
cm) or greater stretched mesh) in the
Southeast U.S. Restricted Area S and
Other Southeast Gillnet Waters must be
marked with a yellow marking.
(B) Markings. All specified gear in
specified areas must be marked with
one color code described in paragraph
(b)(2)(ii)(A) of this section (which
indicates the gear type and general area
where the gear is set). Each color code
must be permanently affixed on or along
the line or lines. Each color code must
be clearly visible when the gear is
hauled or removed from the water. Each
mark must be at least 4 inches (10.2 cm)
long and be placed midway on the buoy
line in the water column. If the color of
the rope is the same as or similar to a
color code, a white mark may be
substituted for that color code. In
marking or affixing the color code, the
line may be dyed, painted, or marked
with thin colored whipping line, thin
colored plastic, or heat-shrink tubing, or
other material; or a thin line may be
woven into or through the line; or the
line may be marked as approved in
writing by the Assistant Administrator.
A brochure illustrating the techniques
for marking gear is available from the
Regional Administrator, NMFS,
Northeast Region upon request.
(iii) Requirements for all specified
areas—(A) Surface buoy markings.
Trap/pot and gillnet gear regulated
under this section must mark all surface
buoys to identify the vessel or fishery
with one of the following: The owner’s
motorboat registration number, the
owner’s U.S. vessel documentation
number, the federal commercial fishing
permit number, or whatever positive
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
identification marking is required by the
vessel’s home-port state. When marking
of surface buoys is not already required
by state or federal regulations, the letters
and numbers used to mark the gear to
identify the vessel or fishery must be at
least 1 inch (2.5 cm) in height in block
letters or arabic numbers in a color that
contrasts with the background color of
the buoy. A brochure illustrating the
techniques for marking gear is available
upon from the Regional Administrator,
NMFS, Northeast Region upon request.
(3) Changes to requirements. If the
Assistant Administrator revises the gear
marking requirements in accordance
with paragraph (i) of this section, the
gear must be marked in compliance
with those requirements.
(c) Restrictions applicable to trap/pot
gear in regulated waters—(1) Universal
trap/pot gear requirements. In addition
to the area-specific measures listed in
paragraphs (c)(2) through (c)(9) of this
section, all trap/pot gear in regulated
waters, including the Northern Inshore
State Trap/Pot Waters Area, must
comply with the universal gear
requirements listed here.1 The Assistant
Administrator may revise these
requirements in accordance with
paragraph (i) of this section.
(i) No buoy line floating at the
surface. No person or vessel may fish
with trap/pot gear that has any portion
of the buoy line floating at the surface
at any time when the buoy line is
directly connected to the gear at the
ocean bottom. If more than one buoy is
attached to a single buoy line or if a
high flyer and a buoy are used together
on a single buoy line, floating line may
be used between these objects.
(ii) No wet storage of gear. Trap/pot
gear must be hauled out of the water at
least once every 30 days.
(2) Cape Cod Bay Restricted Area—(i)
Area. The Cape Cod Bay restricted area
consists of the Cape Cod Bay right
whale critical habitat area specified
under 50 CFR 226.203(b) unless the
Assistant Administrator changes that
area in accordance with paragraph (i) of
this section.
(ii) Area-specific gear or vessel
requirements during the winter
restricted period. No person or vessel
may fish with or possess trap/pot gear
in the Cape Cod Bay Restricted Area
during the winter restricted period
unless that gear complies with the gear
marking requirements specified in
paragraph (b) of this section, the
universal trap/pot gear requirements
1 Fishermen are also encouraged to maintain their
buoy lines to be as knot-free as possible. Splices are
considered to be less of an entanglement threat and
are thus preferable to knots.
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57183
specified in paragraph (c)(1) of this
section, and the area-specific
requirements listed below for the winter
restricted period, or unless the gear is
stowed as specified in
§ 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(A) Winter restricted period. The
winter restricted period for the Cape
Cod Bay Restricted Area is from January
1 through May 15 of each year unless
the Assistant Administrator changes this
period in accordance with paragraph (i)
of this section.
(B) Buoy line weak links. All buoys,
flotation devices and/or weights (except
traps/pots, anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc., must be
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
operationally feasible and that meets the
following specifications:
(1) The breaking strength of the weak
links must not exceed 500 lb (226.8 kg).
(2) The weak link must be chosen
from the following list approved by
NMFS: Swivels, plastic weak links, rope
of appropriate breaking strength, hog
rings, rope stapled to a buoy stick, or
other materials or devices approved in
writing by the Assistant Administrator.
A brochure illustrating the techniques
for making weak links is available from
the Regional Administrator, NMFS,
Northeast Region upon request.
(3) Weak links must break cleanly
leaving behind the bitter end of the line.
The bitter end of the line must be free
of any knots when the weak link breaks.
Splices are not considered to be knots
for the purposes of this provision.
(C) Single traps and multiple-trap
trawls. Single traps and three-trap trawls
are prohibited. All traps must be set in
either a two-trap string or in a trawl of
four or more traps. A two-trap string
must have no more than one buoy line.
(D) Buoy lines. All buoy lines must be
composed of sinking and/or neutrally
buoyant line except the bottom portion
of the line, which may be a section of
floating line not to exceed one-third the
overall length of the buoy line.
(E) Groundlines. All groundlines must
be comprised entirely of sinking and/or
neutrally buoyant line. The attachment
of buoys, toggles, or other floatation
devices to groundlines is prohibited.
(iii) Area-specific gear or vessel
requirements for the other restricted
period. No person or vessel may fish
with or possess trap/pot gear in the
Cape Cod Bay Restricted Area during
the other restricted period unless that
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Federal Register / Vol. 72, No. 193 / Friday, October 5, 2007 / Rules and Regulations
gear complies with the gear marking
requirements specified in paragraph (b)
of this section and the universal trap/
pot gear requirements specified in
paragraph (c)(1) of this section as well
as the area-specific requirements listed
below for the other restricted period, or
unless the gear is stowed as specified in
§ 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(A) Other restricted period. The other
restricted period for the Cape Cod Bay
Restricted Area is from May 16 through
December 31 of each year unless the
Assistant Administrator revises this
period in accordance with paragraph (i)
of this section.
(B) Gear and vessel requirements—(1)
State-water portion. No person or vessel
may fish with or possess trap/pot gear
in the state-water portion of the Cape
Cod Bay Restricted Area during the
other restricted period unless that gear
complies with the requirements for the
Northern Inshore State Trap/Pot Waters
Area listed in paragraph (c)(6) of this
section, or unless the gear is stowed as
specified in § 229.2. The Assistant
Administrator may revise these
requirements in accordance with
paragraph (i) of this section.
(2) Federal-water portion. No person
or vessel may fish with or possess trap/
pot gear in the Federal-water portion of
the Cape Cod Bay Restricted Area
during the other restricted period unless
that gear complies with the
requirements for the Northern
Nearshore Trap/Pot Waters Area in
paragraph (c)(7) of this section, or
unless the gear is stowed as specified in
§ 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(3) Great South Channel Restricted
Trap/Pot Area—(i) Area. The Great
South Channel Restricted Trap/Pot Area
consists of the Great South Channel
right whale critical habitat area
specified under 50 CFR 226.203(a)
unless the Assistant Administrator
changes that area in accordance with
paragraph (i) of this section.
(ii) Closure during the spring
restricted period. The spring restricted
period for the Great South Channel
Restricted Trap/Pot Area is from April
1 through June 30 of each year unless
the Assistant Administrator revises this
period in accordance with paragraph (i)
of this section. During the spring
restricted period, no person or vessel
may fish with, set, or possess trap/pot
gear in this Area unless the Assistant
Administrator specifies gear
modifications or alternative fishing
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
practices in accordance with paragraph
(i) of this section and the gear or
practices comply with those
specifications, or unless the gear is
stowed as specified in § 229.2.
(iii) Area-specific gear or vessel
requirements for the other restricted
period. The other restricted period for
the Great South Channel Restricted
Trap/Pot Area is July 1 through March
31, unless the Assistant Administrator
revises this period in accordance with
paragraph (i) of this section. During the
other restricted period, no person or
vessel may fish with or possess trap/pot
gear in the Great South Channel
Restricted Trap/Pot Area unless that
gear complies with the gear marking
requirements specified in paragraph (b)
of this section, and the universal trap/
pot gear requirements specified in
paragraph (c)(1) of this section, or
unless the gear is stowed as specified in
§ 229.2. Additionally, no person or
vessel may fish with or possess trap/pot
gear in the Great South Channel
Restricted Trap/Pot Area unless that
gear complies with the requirements
listed for Northern Nearshore Trap/Pot
Waters Area in paragraph (c)(7) of this
section where the Great South Channel
Restricted Trap/Pot Area overlaps with
Lobster Management Area (LMA) 2 and
the Outer Cape LMA (as defined in the
American Lobster Fishery regulations in
50 CFR 697.18); the requirements listed
for Offshore Trap/Pot Waters in
paragraph (c)(5) of this section where
the Great South Channel Restricted
Trap/Pot Area overlaps with LMA 2/3
Overlap and LMA 3 (as defined in the
American Lobster Fishery regulations in
50 CFR 697.18); or unless the gear is
stowed as specified in § 229.2. The
Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(4) Stellwagen Bank/Jeffreys Ledge
Restricted Area—(i) Area. The
Stellwagen Bank/Jeffreys Ledge
Restricted Area includes all Federal
waters of the Gulf of Maine, except
those designated as right whale critical
habitat under 50 CFR 226.203(b), that lie
south of 43°15′ N. lat. and west of 70°00′
W. long. The Assistant Administrator
may change that area in accordance
with paragraph (i) of this section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess trap/pot gear
in the Stellwagen Bank/Jeffreys Ledge
Restricted Area unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, the universal trap/pot
gear requirements specified in
paragraph (c)(1) of this section, and the
requirements listed for the Northern
PO 00000
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Nearshore Trap/Pot Waters Area
specified in paragraph (c)(7) of this
section, or unless the gear is stowed as
specified in § 229.2. The Assistant
Administrator may revise these
requirements in accordance with
paragraph (i) of this section.
(5) Offshore Trap/Pot 2 Waters Area—
(i) Area. The Offshore Trap/Pot Waters
Area includes all Federal waters of the
EEZ Offshore Management Area 3
(including the area known as the Area
2⁄3 Overlap and Area 3⁄5 Overlap as
defined in the American Lobster Fishery
regulations at 50 CFR 697.18, with the
exception of the Great South Channel
Restricted Trap/Pot Area), and
extending south along the 100-fathom
(600-ft or 182.9-m) depth contour from
35°30′ N. lat. south to 27°51′ N. lat., and
east to the eastern edge of the EEZ. The
Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess trap/pot gear
in the Offshore Trap/Pot Waters Area
that overlaps an area from the
U.S./Canada border south to a straight
line from 41°18.2′ N. lat., 71°51.5′ W.
long. (Watch Hill Point, RI) south to
40°00′ N. lat., and then east to the
eastern edge of the EEZ, unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, the universal trap/pot
gear requirements specified in
paragraph (c)(1) of this section, and the
area-specific requirements listed below,
or unless the gear is stowed as specified
in § 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(A) Buoy line weak links. All buoys,
flotation devices and/or weights (except
traps/pots, anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc., must be
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
operationally feasible and that meets the
following specifications:
(1) The weak link must be chosen
from the following list approved by
NMFS: Swivels, plastic weak links, rope
of appropriate breaking strength, hog
rings, rope stapled to a buoy stick, or
other materials or devices approved in
writing by the Assistant Administrator.
A brochure illustrating the techniques
for making weak links is available from
2 Fishermen using red crab trap/pot gear should
refer to § 229.32(c)(9) for the restrictions applicable
to red crab trap/pot fishery.
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the Regional Administrator, NMFS,
Northeast Region upon request.
(2) The breaking strength of the weak
links may not exceed 1,500 lb (680.4
kg).
(3) Weak links must break cleanly
leaving behind the bitter end of the line.
The bitter end of the line must be free
of any knots when the weak link breaks.
Splices are not considered to be knots
for the purposes of this provision.
(B) Groundlines. On or before October
6, 2008, all groundlines must be
comprised entirely of sinking and/or
neutrally buoyant line unless exempted
from this requirement under paragraph
(a)(4) of this section. The attachment of
buoys, toggles, or other flotation devices
to groundlines is prohibited.
(iii) Seasonal area-specific gear or
vessel requirements. From September 1
to May 31, no person or vessel may fish
with or possess trap/pot gear in the
Offshore Trap/Pot Waters Area that
overlaps an area bounded on the north
by a straight line from 41°18.2′ N. lat.,
71°51.5′ W. long. (Watch Hill Point, RI)
south to 40°00′ N. lat. and then east to
the eastern edge of the EEZ, and
bounded on the south by a line at 32°00′
N. lat., and east to the eastern edge of
the EEZ, unless that gear complies with
the gear marking requirements specified
in paragraph (b) of this section, the
universal trap/pot gear requirements
specified in paragraph (c)(1) of this
section, the area-specific requirements
specified in paragraphs (c)(5)(ii)(A) and
(c)(5)(ii)(B) of this section, or unless the
gear is stowed as specified in § 229.2.
The Assistant Administrator may revise
that period and these requirements in
accordance with paragraph (i) of this
section.
(iv) Seasonal area-specific gear or
vessel requirements. From November 15
to April 15, no person or vessel may fish
with or possess trap/pot gear in the
Offshore Trap/Pot Waters Area that
overlaps an area from 32°00′ N. lat.
south to 29°00′ N. lat. and east to the
eastern edge of the EEZ, unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, the universal trap/pot
gear requirements specified in
paragraph (c)(1) of this section, and the
area-specific requirements specified in
paragraphs (c)(5)(ii)(A) and (c)(5)(ii)(B)
of this section, or unless the gear is
stowed as specified in § 229.2. The
Assistant Administrator may revise that
period and these requirements in
accordance with paragraph (i) of this
section.
(v) Seasonal area-specific gear or
vessel requirements. From December 1
to March 31, no person or vessel may
fish with or possess trap/pot gear in the
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
Offshore Trap/Pot Waters Area that
overlaps an area from 29°00′ N. lat.
south to 27°51′ N. lat. and east to the
eastern edge of the EEZ, unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, the universal trap/pot
gear requirements specified in (c)(1) of
this section, and the area-specific
requirements specified in paragraphs
(c)(5)(ii)(A) and (c)(5)(ii)(B) of this
section, or unless the gear is stowed as
specified in § 229.2. The Assistant
Administrator may revise this period
and these requirements in accordance
with paragraph (i) of this section.
(vi) [Reserved]
(6) Northern Inshore State Trap/Pot
Waters Area—(i) Area. The Northern
Inshore State Trap/Pot Waters Area
includes the state waters of Rhode
Island, Massachusetts, New Hampshire,
and Maine, with the exception of Cape
Cod Bay Restricted Area and those
waters exempted under paragraph (a)(3)
of this section. The Assistant
Administrator may change that area in
accordance with paragraph (i) of this
section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess trap/pot gear
in the Northern Inshore State Trap/Pot
Waters Area unless that gear complies
with the gear marking requirements
specified in paragraph (b) of this
section, the universal trap/pot gear
requirements specified in paragraph
(c)(1) of this section, and the areaspecific requirements listed below, or
unless the gear is stowed as specified in
§ 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(A) Buoy line weak links. All buoys,
flotation devices and/or weights (except
traps/pots, anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc., must be
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
operationally feasible and that meets the
following specifications:
(1) The weak link must be chosen
from the following list approved by
NMFS: swivels, plastic weak links, rope
of appropriate breaking strength, hog
rings, rope stapled to a buoy stick, or
other materials or devices approved in
writing by the Assistant Administrator.
A brochure illustrating the techniques
for making weak links is available from
the Regional Administrator, NMFS,
Northeast Region upon request.
(2) The breaking strength of the weak
links may not exceed 600 lb (272.2 kg).
PO 00000
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57185
(3) Weak links must break cleanly
leaving behind the bitter end of the line.
The bitter end of the line must be free
of any knots when the weak link breaks.
Splices are not considered to be knots
for the purposes of this provision.
(B) Groundlines. On or before October
6, 2008, all groundlines must be
comprised entirely of sinking and/or
neutrally buoyant line unless exempted
for this requirement under paragraph
(a)(4) of this section. The attachment of
buoys, toggles, or other flotation devices
to groundlines is prohibited.
(C) [Reserved]
(7) Northern Nearshore Trap/Pot
Waters Area—(i) Area. The Northern
Nearshore Trap/Pot Waters Area
includes all Federal waters of EEZ
Nearshore Management Area 1, Area 2,
and the Outer Cape Lobster
Management Area (as defined in the
American Lobster Fishery regulations at
50 CFR 697.18), with the exception of
the Great South Channel Restricted
Trap/Pot Area, Cape Cod Bay Restricted
Area, Stellwagen Bank/Jeffreys Ledge
Restricted Area and those waters
exempted under paragraph (a)(3) of this
section. The Assistant Administrator
may change that area in accordance
with paragraph (i) of this section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess trap/pot gear
in the Northern Nearshore Trap/Pot
Waters Area unless that gear complies
with the gear marking requirements
specified in paragraph (b) of this
section, the universal trap/pot gear
requirements specified in paragraph
(c)(1) of this section, and the areaspecific requirements listed below, or
unless the gear is stowed as specified in
§ 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(A) Buoy line weak links. All buoys,
flotation devices and/or weights (except
traps/pots, anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc., must be
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
operationally feasible and that meets the
following specifications:
(1) The weak link must be chosen
from the following list approved by
NMFS: swivels, plastic weak links, rope
of appropriate breaking strength, hog
rings, rope stapled to a buoy stick, or
other materials or devices approved in
writing by the Assistant Administrator.
A brochure illustrating the techniques
for making weak links is available from
E:\FR\FM\05OCR2.SGM
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57186
Federal Register / Vol. 72, No. 193 / Friday, October 5, 2007 / Rules and Regulations
the Regional Administrator, NMFS,
Northeast Region upon request.
(2) The breaking strength of the weak
links must not exceed 600 lb (272.2 kg).
(3) Weak links must break cleanly
leaving behind the bitter end of the line.
The bitter end of the line must be free
of any knots when the weak link breaks.
Splices are not considered to be knots
for the purposes of this provision.
(B) Single traps and multiple-trap
trawls. Single traps are prohibited. All
traps must be set in trawls of two or
more traps. All trawls up to and
including five traps must have no more
than one buoy line.
(C) Groundlines. On or before October
6, 2008, all groundlines must be
comprised entirely of sinking and/or
neutrally buoyant line unless exempted
from this requirement under paragraph
(a)(4) of this section. The attachment of
buoys, toggles, or other floatation
devices to groundlines is prohibited.
(D) [Reserved]
(8) Southern Nearshore3 Trap/Pot
Waters Area—(i) Area. The Southern
Nearshore Trap/Pot Waters Area
includes all state and Federal waters
which fall within EEZ Nearshore
Management Area 4, EEZ Nearshore
Management Area 5, and EEZ Nearshore
Management Area 6 (as defined in the
American Lobster Fishery regulations in
50 CFR 697.18), and inside the 100fathom (600-ft or 182.9-m) depth
contour line from 35°30′ N lat. south to
27°51′ N lat. and extending inshore to
the shoreline or exemption line, with
the exception of those waters exempted
under paragraph (a)(3) of this section.
The Assistant Administrator may
change that area in accordance with
paragraph (i) of this section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess trap/pot gear
in the Southern Nearshore Trap/Pot
Waters Area that is east of a straight line
from 41°18.2′ N. lat.,71°51.5′ W. long.
(Watch Hill Point, RI) south to 40°00′ N.
lat., unless that gear complies with the
gear marking requirements specified in
paragraph (b) of this section, the
universal trap/pot gear requirements
specified in paragraph (c)(1) of this
section, and the area-specific
requirements listed here, or unless the
gear is stowed as specified in § 229.2.
The Assistant Administrator may revise
that period and these requirements in
accordance with paragraph (i) of this
section.
(A) Buoy line weak links. All buoys,
flotation devices and/or weights (except
3 Fishermen using red crab trap/pot gear should
refer to § 229.32(c)(9) for the restrictions applicable
to red crab trap/pot fishery.
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
traps/pots, anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc., must be
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
operationally feasible and that meets the
following specifications:
(1) The weak link must be chosen
from the following list approved by
NMFS: swivels, plastic weak links, rope
of appropriate breaking strength, hog
rings, rope stapled to a buoy stick, or
other materials or devices approved in
writing by the Assistant Administrator.
A brochure illustrating the techniques
for making weak links is available from
the Regional Administrator, NMFS,
Northeast Region upon request.
(2) The breaking strength of the weak
links may not exceed 600 lb (272.2 kg).
(3) Weak links must break cleanly
leaving behind the bitter end of the line.
The bitter end of the line must be free
of any knots when the weak link breaks.
Splices are not considered to be knots
for the purposes of this provision.
(B) Groundlines. On or before October
6, 2008, all groundlines must be
comprised entirely of sinking and/or
neutrally buoyant line unless exempted
from this requirement under paragraph
(a)(4) of this section. The attachment of
buoys, toggles, or other floatation
devices to groundlines is prohibited.
(iii) Seasonal area-specific gear or
vessel requirements. From September 1
to May 31, no person or vessel may fish
with or possess trap/pot gear in the
Southern Nearshore Trap/Pot Waters
Area that overlaps an area bounded on
the north by a straight line from 41°18.2′
N. lat., 71°51.5′ W. long. (Watch Hill
Point, RI) south to 40°00′ N. lat. and
then east to the eastern edge of the EEZ,
and bounded on the south by 32°00′ N.
lat., and east to the eastern edge of the
EEZ, unless that gear complies with the
gear marking requirements specified in
paragraph (b) of this section, the
universal trap/pot gear requirements in
paragraph (c)(1) of this section,
requirements specified in paragraphs
(c)(8)(ii)(A) and (c)(8)(ii)(B) of this
section, or unless the gear is stowed as
specified in § 229.2. The Assistant
Administrator may revise that period
and these requirements in accordance
with paragraph (i) of this section.
(iv) Seasonal area-specific gear or
vessel requirements. From November 15
to April 15, no person or vessel may fish
with or possess trap/pot gear in the
Southern Nearshore Trap/Pot Waters
Area that overlaps an area from 32°00′
N. lat. south to 29°00′ N. lat. and east
to the eastern edge of the EEZ, unless
that gear complies with the gear
PO 00000
Frm 00084
Fmt 4701
Sfmt 4700
marking requirements specified in
paragraph (b) of this section, the
universal trap/pot gear requirements
specified in paragraph (c)(1) of this
section, and the area-specific
requirements specified in paragraphs
(c)(8)(ii)(A) and (c)(8)(ii)(B) of this
section, or unless the gear is stowed as
specified in § 229.2. The Assistant
Administrator may revise that period
and these requirements in accordance
with paragraph (i) of this section.
(v) Seasonal area-specific gear or
vessel requirements. From December 1
to March 31, no person or vessel may
fish with or possess trap/pot gear in the
Southern Nearshore Trap/Pot Waters
Area that overlaps an area from 29°00′
N. lat. south to 27°51′ N. lat. and east
to the eastern edge of the EEZ, unless
that gear complies with the gear
marking requirements specified in
paragraph (b) of this section, the
universal trap/pot gear requirements
specified in paragraph (c)(1) of this
section, and the area-specific
requirements specified in paragraphs
(c)(8)(ii)(A) and (c)(8)(ii)(B) of this
section, or unless the gear is stowed as
specified in § 229.2. The Assistant
Administrator may revise this period
and these requirements in accordance
with paragraph (i) of this section.
(vi) [Reserved]
(9) Restrictions applicable to the red
crab trap/pot fishery—(i) Area. The red
crab trap/pot fishery is regulated in the
waters identified in paragraphs (c)(5)(i)
and (c)(8)(i) of this section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess red crab trap/
pot gear in the area identified in
paragraph (c)(9)(i) of this section that
overlaps an area from the U.S./Canada
border south to a straight line from 41°
18.2′ N. lat., 71°51.5′ W. long. (Watch
Hill Point, RI) south to 40°00′ N. lat.,
and then east to the eastern edge of the
EEZ, unless that gear complies with the
gear marking requirements specified in
paragraph (b) of this section, the
universal trap/pot gear requirements
specified in paragraph (c)(1) of this
section, and the area-specific
requirements listed below, or unless the
gear is stowed as specified in § 229.2.
The Assistant Administrator revises
these requirements in accordance with
paragraph (i) of this section.
(A) Buoy line weak links. All buoys,
flotation devices and/or weights (except
traps/pots, anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc., must be
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
E:\FR\FM\05OCR2.SGM
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operationally feasible and that meets the
following specifications:
(1) The weak link must be chosen
from the following list approved by
NMFS: Swivels, plastic weak links, rope
of appropriate breaking strength, hog
rings, rope stapled to a buoy stick, or
other materials or devices approved in
writing by the Assistant Administrator.
A brochure illustrating the techniques
for making weak links is available from
the Regional Administrator, NMFS,
Northeast Region upon request.
(2) The breaking strength of the weak
links may not exceed 2,000 lb (907.2
kg).
(3) Weak links must break cleanly
leaving behind the bitter end of the line.
The bitter end of the line must be free
of any knots when the weak link breaks.
Splices are not considered to be knots
for the purposes of this provision.
(B) Groundlines. On or before October
6, 2008, all groundlines must be
comprised entirely of sinking and/or
neutrally buoyant line unless exempted
from this requirement under paragraph
(a)(4) of this section. The attachment of
buoys, toggles, or other floatation
devices to groundlines is prohibited.
(iii) Seasonal area-specific gear or
vessel requirements. From September 1
to May 31, no person or vessel may fish
with or possess red crab trap/pot gear in
the area identified in paragraph (c)(9)(i)
of this section that overlaps an area
bounded on the north by a straight line
from 41°18.2′ N. lat., 71°51.5′ W. long.
(Watch Hill Point, RI) south to 40°00′ N.
lat. and then east to the eastern edge of
the EEZ, and bounded on the south by
a line at 32°00′ N. lat., and east to the
eastern edge of the EEZ, unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, the universal trap/pot
gear requirements specified in
paragraph (c)(1) of this section, and the
area-specific requirements listed in
paragraphs (c)(9)(ii)(A) and (c)(9)(ii)(B)
of this section, or unless the gear is
stowed as specified in § 229.2. The
Assistant Administrator revises these
requirements in accordance with
paragraph (i) of this section.
(iv) Seasonal area-specific gear or
vessel requirements. From November 15
to April 15, no person or vessel may fish
with or possess red crab trap/pot gear in
the area identified in paragraph (c)(9)(i)
of this section that overlaps an area from
32°00′ N. lat. south to 29°00′ N. lat. and
east to the eastern edge of the EEZ,
unless that gear complies with the gear
marking requirements specified in
paragraph (b) of this section, the
universal trap/pot gear requirements
specified in paragraph (c)(1) of this
section, and the area-specific
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
requirements specified in paragraphs
(c)(9)(ii)(A) and (c)(9)(ii)(B) of this
section, or unless the gear is stowed as
specified in § 229.2. The Assistant
Administrator may revise that period
and these requirements in accordance
with paragraph (i) of this section.
(v) Seasonal area-specific gear or
vessel requirements. From December 1
to March 31, no person or vessel may
fish with or possess red crab trap/pot
gear in the area identified in paragraph
(c)(9)(i) of this section that overlaps an
area from 29°00′ N. lat. south to 27°51′
N. lat. and east to the eastern edge of the
EEZ, unless that gear complies with the
gear marking requirements specified in
paragraph (b) of this section, the
universal trap/pot gear requirements
specified in paragraph (c)(1) of this
section, and the area-specific
requirements specified in paragraphs
(c)(9)(ii)(A) and (c)(9)(ii)(B) of this
section, or unless the gear is stowed as
specified in § 229.2. The Assistant
Administrator may revise that period
and these requirements in accordance
with paragraph (i) of this section.
(vi) [Reserved]
(d) Restrictions applicable to
anchored gillnet gear—(1) Universal
anchored gillnet gear requirements. In
addition to the area-specific measures
listed in paragraphs (d)(2) through (d)(7)
of this section, all anchored gillnet gear
in regulated waters must comply with
the universal gear requirements listed
here. 4 The Assistant Administrator may
revise these requirements in accordance
with paragraph (i) of this section.
(i) No buoy line floating at the
surface. No person or vessel may fish
with anchored gillnet gear that has any
portion of the buoy line floating at the
surface at any time when the buoy line
is directly connected to the gear at the
ocean bottom. If more than one buoy is
attached to a single buoy line or if a
high flyer and a buoy are used together
on a single buoy line, sinking and/or
neutrally buoyant line must be used
between these objects.
(ii) No wet storage of gear. Anchored
gillnet gear must be hauled out of the
water at least once every 30 days.
(2) Cape Cod Bay Restricted Area—(i)
Area. The Cape Cod Bay Restricted Area
consists of the Cape Cod Bay right
whale critical habitat area specified
under 50 CFR 226.203(b), unless the
Assistant Administrator changes that
area in accordance with paragraph (i) of
this section.
(ii) Closure during the winter
restricted period—(A) Winter restricted
4 Fishermen are also encouraged to maintain their
buoy lines to be as knot-free as possible. Splices are
considered to be less of an entanglement threat and
are thus preferable to knots.
PO 00000
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57187
period. The winter restricted period for
this area is from January 1 through May
15 of each year, unless the Assistant
Administrator revises that period in
accordance with paragraph (i) of this
section.
(B) Closure. During the winter
restricted period, no person or vessel
may fish with or possess anchored
gillnet gear in the Cape Cod Bay
Restricted Area unless the Assistant
Administrator specifies gear restrictions
or alternative fishing practices in
accordance with paragraph (i) of this
section and the gear or practices comply
with those specifications, or unless the
gear is stowed as specified in § 229.2.
The Assistant Administrator may waive
this closure for the remaining portion of
the winter restricted period in any year
through a notification in the Federal
Register if NMFS determines that right
whales have left the restricted area and
are unlikely to return for the remainder
of the season.
(iii) Area-specific gear or vessel
requirements for the other restricted
period—(A) Other restricted period. The
other restricted period for the Cape Cod
Bay Restricted Area is from May 16
through December 31 of each year
unless the Assistant Administrator
changes that period in accordance with
paragraph (i) of this section.
(B) Area-specific gear or vessel
requirements. No person or vessel may
fish with or possess anchored gillnet
gear in the Cape Cod Bay Restricted
Area during the other restricted period
unless that gear complies with the gear
marking requirements specified in
paragraph (b) of this section, the
universal anchored gillnet gear
requirements specified in paragraph
(d)(1) of this section, and the areaspecific requirements listed in
paragraph (d)(6)(ii) of this section for
the Other Northeast Gillnet Waters Area,
or unless the gear is stowed as specified
in § 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(3) Great South Channel Restricted
Gillnet Area—(i) Area. The Great South
Channel Restricted Gillnet Area consists
of the area bounded by lines connecting
the following four points: 41°02.2′ N.
lat./69°02′ W. long., 41°43.5′ N. lat./
69°36.3′ W. long., 42°10′ N. lat./68°31′
W. long., and 41°38′ N. lat./68°13′ W.
long. This area includes most of the
Great South Channel right whale critical
habitat area specified under 50 CFR
226.203(a), with the exception of the
sliver along the western boundary
described in paragraph (d)(4)(i) of this
section. The Assistant Administrator
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may change that area in accordance
with paragraph (i) of this section.
(ii) Closure during the spring
restricted period—(A) Spring restricted
period. The spring restricted period for
the Great South Channel Restricted
Gillnet Area is from April 1 through
June 30 of each year unless the Assistant
Administrator revises that period in
accordance with paragraph (i) of this
section.
(B) Closure. During the spring
restricted period, no person or vessel
may set, fish with or possess anchored
gillnet gear in the Great South Channel
Restricted Gillnet Area unless the
Assistant Administrator specifies gear
restrictions or alternative fishing
practices in accordance with paragraph
(i) of this section and the gear or
practices comply with those
specifications, or unless the gear is
stowed as specified in § 229.2.
(iii) Area-specific gear or vessel
requirements for the other restricted
period—(A) Other restricted period. The
other restricted period for the Great
South Channel Restricted Gillnet Area is
from July 1 though March 31 of each
year unless the Assistant Administrator
changes that period in accordance with
paragraph (i) of this section.
(B) Area-specific gear or vessel
requirements. During the other
restricted period, no person or vessel
may fish with or possess anchored
gillnet gear in the Great South Channel
Restricted Gillnet Area unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, the universal anchored
gillnet gear requirements specified in
paragraph (d)(1) of this section, and the
area-specific requirements listed in
paragraph (d)(6)(ii) of this section for
the Other Northeast Gillnet Waters Area,
or unless the gear is stowed as specified
in § 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(4) Great South Channel Sliver
Restricted Area—(i) Area. The Great
South Channel Sliver Restricted Area
consists of the area bounded by lines
connecting the following points:
41°02.2′ N. lat./69°02′ W. long., 41°43.5′
N. lat./69°36.3′ W. long., 41°40′ N. lat./
69°45′ W. long., and 41°00′ N. lat./
69°05′ W. long. The Assistant
Administrator may change that area in
accordance with paragraph (i) of this
section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess anchored
gillnet gear in the Great South Channel
Sliver Restricted Area unless that gear
complies with the gear marking
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15:40 Oct 04, 2007
Jkt 214001
requirements specified in paragraph (b)
of this section, the universal anchored
gillnet gear requirements specified in
paragraph (d)(1) of this section, and the
area-specific requirements listed in
paragraph (d)(6)(ii) of this section for
the Other Northeast Gillnet Waters Area,
or unless the gear is stowed as specified
in § 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(5) Stellwagen Bank/Jeffreys Ledge
Restricted Area—(i) Area. The
Stellwagen Bank/Jeffreys Ledge
Restricted Area includes all Federal
waters of the Gulf of Maine, except
those designated as right whale critical
habitat under 50 CFR 226.203(b), that lie
south of 43°15′ N. lat. and west of 70°00′
W. long, and those waters exempted
under paragraph (a)(3) of this section.
The Assistant Administrator may
change that area in accordance with
paragraph (i) of this section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess anchored
gillnet gear in the Stellwagen Bank/
Jeffreys Ledge Restricted Area unless
that gear complies with the gear
marking requirements specified in
paragraph (b) of this section, the
universal anchored gillnet gear
requirements specified in paragraph
(d)(1) of this section, and the areaspecific requirements listed in
paragraph (d)(6)(ii) of this section for
the Other Northeast Gillnet Waters Area,
or unless the gear is stowed as specified
in § 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(6) Other Northeast Gillnet Waters
Area—(i) Area. The Other Northeast
Gillnet Waters Area consists of all U.S.
waters from the U.S./Canada border to
Long Island, NY, at 72°30′ W. long.
south to 36°33.03′ N. lat. and east to the
eastern edge of the EEZ, with the
exception of the Cape Cod Bay
Restricted Area, Stellwagen Bank/
Jeffreys Ledge Restricted Area, Great
South Channel Restricted Gillnet Area,
Great South Channel Sliver Restricted
Area, and exempted waters listed in
paragraph (a)(3) of this section. The
Assistant Administrator may change
that area in accordance with paragraph
(i) of this section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess anchored
gillnet gear in the Other Northeast
Gillnet Waters Area that overlaps an
area from the U.S./Canada border south
to a straight line from 41°18.2′ N. lat.,
71°51.5′ W. long. (Watch Hill Point, RI)
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Fmt 4701
Sfmt 4700
south to 40°00′ N. lat. and then east to
the eastern edge of the EEZ, unless that
gear complies with the gear marking
requirements specified in paragraph (b)
of this section, the universal anchored
gillnet gear requirements specified in
paragraph (d)(1) of this section, and the
area-specific requirements listed below,
or unless the gear is stowed as specified
in § 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section.
(A) Buoy line weak links. All buoys,
flotation devices and/or weights (except
gillnets, anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc., must be
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
operationally feasible and that meets the
following specifications:
(1) The weak link must be chosen
from the following list approved by
NMFS: Swivels, plastic weak links, rope
of appropriate breaking strength, hog
rings, rope stapled to a buoy stick, or
other materials or devices approved in
writing by the Assistant Administrator.
A brochure illustrating the techniques
for making weak links is available from
the Regional Administrator, NMFS,
Northeast Region upon request.
(2) The breaking strength of the weak
links must not exceed 1,100 lb (499.0
kg).
(3) Weak links must break cleanly
leaving behind the bitter end of the line.
The bitter end of the line must be free
of any knots when the weak link breaks.
Splices are not considered to be knots
for the purposes of this provision.
(B) Net panel weak links. The
breaking strength of each weak link
must not exceed 1,100 lb (499.0 kg). The
weak link requirements apply to all
variations in panel size. All net panels
in a string must contain weak links that
meet one of the following two
configurations:
(1) Configuration 1. (i) The weak link
must be chosen from the following list
approved by NMFS: Plastic weak links
or rope of appropriate breaking strength.
If rope of appropriate breaking strength
is used throughout the floatline or as the
up and down line, or if no up and down
line is present, then individual weak
links are not required on the floatline or
up and down line. A brochure
illustrating the techniques for making
weak links is available from the
Regional Administrator, NMFS,
Northeast Region upon request; and
(ii) One weak link must be placed in
the center of each of the up and down
lines at both ends of the net panel; and
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(iii) One weak link must be placed as
close as possible to each end of the net
panels on the floatline; and
(iv) For net panels of 50 fathoms (300
ft or 91.4 m) or less in length, one weak
link must be placed in the center of the
floatline; or
(v) For net panels greater than 50
fathoms (300 ft or 91.4 m) in length, one
weak link must be placed at least every
25 fathoms (150 ft or 45.7 m) along the
floatline.
(2) Configuration 2. (i) The weak link
must be chosen from the following list
approved by NMFS: Plastic weak links
or rope of appropriate breaking strength.
If rope of appropriate breaking strength
is used throughout the floatline or as the
up and down line, or if no up and down
line is present, then individual weak
links are not required on the floatline or
up and down line. A brochure
illustrating the techniques for making
weak links is available from the
Regional Administrator, NMFS,
Northeast Region upon request; and
(ii) One weak link must be placed in
the center of each of the up and down
lines at both ends of the net panel; and
(iii) One weak link must be placed
between the floatline tie loops between
net panels; and
(iv) One weak link must be placed
where the floatline tie loops attaches to
the bridle, buoy line, or groundline at
the end of a net string; and
(v) For net panels of 50 fathoms (300
ft or 91.4 m) or less in length, one weak
link must be placed in the center of the
floatline; or
(vi) For net panels greater than 50
fathoms (300 ft or 91.4 m) in length, one
weak link must be placed at least every
25 fathoms (150 ft or 45.7 m) along the
floatline.
(C) Anchoring systems. All anchored
gillnets, regardless of the number of net
panels, must be secured at each end of
the net string with a burying anchor (an
anchor that holds to the ocean bottom
through the use of a fluke, spade, plow,
or pick) having the holding capacity
equal to or greater than a 22-lb (10.0-kg)
Danforth-style anchor. Dead weights do
not meet this requirement. A brochure
illustrating the techniques for rigging
anchoring systems is available from the
Regional Administrator, NMFS,
Northeast Region upon request.
(D) Groundlines. On or before October
6, 2008, all groundlines must be
comprised entirely of sinking and/or
neutrally buoyant line unless exempted
from this requirement under paragraph
(a)(4) of this section. The attachment of
buoys, toggles, or other floatation
devices to groundlines is prohibited.
(iii) Seasonal area-specific gear or
vessel requirements. From September 1
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15:40 Oct 04, 2007
Jkt 214001
to May 31, no person or vessel may fish
with or possess anchored gillnet gear in
the Other Northeast Gillnet Waters Area
that is south of a straight line from
41°18.2′ N. lat., 71°51.5′ W. long. (Watch
Hill Point, RI) south to 40°00′ N. lat. and
then east to the eastern edge of the EEZ,
unless that gear complies with the gear
marking requirements specified in
paragraph (b) of this section, the
universal anchored gillnet gear
requirements specified in paragraph
(d)(1) of this section, and the areaspecific requirements listed in
paragraphs (d)(6)(ii)(A) through
(d)(6)(ii)(D) of this section, or unless the
gear is stowed as specified in § 229.2.
The Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(7) Mid/South Atlantic Gillnet
Waters—(i) Area. The Mid/South
Atlantic Gillnet Waters consists of all
U.S. waters bounded on the north from
Long Island, NY, at 72°30′ W. long.
south to 36°33.03′ N. lat. and east to the
eastern edge of the EEZ, and bounded
on the south by 32°00′ N. lat., and east
to the eastern edge of the EEZ. The
Assistant Administrator may change
that area in accordance with paragraph
(i) of this section. When the Mid/South
Atlantic Gillnet Waters Area overlaps
the Southeast U.S. Restricted Area and
its restricted period as specified in
paragraphs (f)(1) and (f)(2), then the
closure and exemption for the Southeast
U.S. Restricted Area as specified in
paragraph (f)(2) applies.
(ii) Area-specific gear or vessel
requirements. From September 1
through May 31, no person or vessel
may fish with or possess anchored
gillnet gear in the Mid/South Atlantic
Gillnet Waters unless that gear complies
with the gear marking requirements
specified in paragraph (b) of this
section, the universal anchored gillnet
gear requirements specified in
paragraph (d)(1) of this section, and the
following area-specific requirements, or
unless the gear is stowed as specified in
§ 229.2. The Assistant Administrator
may revise these requirements in
accordance with paragraph (i) of this
section. When the Mid/South Atlantic
Gillnet Waters Area overlaps the
Southeast U.S. Restricted Area and its
restricted period as specified in
paragraphs (f)(1) and (f)(2), then the
closure and exemption for the Southeast
U.S. Restricted Area as specified in
paragraph (f)(2) applies.
(A) Buoy line weak links. All buoys,
flotation devices and/or weights (except
gillnets, anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc., must be
PO 00000
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57189
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
operationally feasible and that meets the
following specifications:
(1) The weak link must be chosen
from the following list approved by
NMFS: Swivels, plastic weak links, rope
of appropriate breaking strength, hog
rings, rope stapled to a buoy stick, or
other materials or devices approved in
writing by the Assistant Administrator.
A brochure illustrating the techniques
for making weak links is available from
the Regional Administrator, NMFS,
Northeast Region upon request.
(2) The breaking strength of the weak
links must not exceed 1,100 lb (499.0
kg).
(3) Weak links must break cleanly
leaving behind the bitter end of the line.
The bitter end of the line must be free
of any knots when the weak link breaks.
Splices are not considered to be knots
for the purposes of this provision.
(B) Net panel weak links. The weak
link requirements apply to all variations
in panel size. All net panels must
contain weak links that meet the
following specifications:
(1) The breaking strength for each of
the weak links must not exceed 1,100 lb
(499.0 kg).
(2) The weak link must be chosen
from the following list approved by
NMFS: Plastic weak links or rope of
appropriate breaking strength. If rope of
appropriate breaking strength is used
throughout the floatline then individual
weak links are not required. A brochure
illustrating the techniques for making
weak links is available from the
Regional Administrator, NMFS,
Northeast Region upon request.
(3) Weak links must be placed in the
center of the floatline of each gillnet net
panel up to and including 50 fathoms
(300 ft or 91.4 m) in length, or at least
every 25 fathoms (150 ft or 45.7 m)
along the floatline for longer panels.
(C) Additional anchoring system and
net panel weak link requirements. All
gillnets must return to port with the
vessel unless the gear meets the
following specifications:
(1) Anchoring systems. All anchored
gillnets, regardless of the number of net
panels, must be secured at each end of
the net string with a burying anchor (an
anchor that holds to the ocean bottom
through the use of a fluke, spade, plow,
or pick) having the holding capacity
equal to or greater than a 22-lb (10.0-kg)
Danforth-style anchor. Dead weights do
not meet this requirement. A brochure
illustrating the techniques for rigging
anchoring systems is available from the
Regional Administrator, NMFS,
Northeast Region upon request.
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(2) Net panel weak links. Net panel
weak links must meet the specifications
in this paragraph. The breaking strength
of each weak link must not exceed 1,100
lb (499.0 kg). The weak link
requirements apply to all variations in
panel size. All net panels in a string
must contain weak links that meet one
of the following two configurations
found in paragraph (d)(6)(ii)(B)(1) or
(d)(6)(ii)(B)(2) of this section.
(3) Additional provision for North
Carolina. All gillnets set 300 yards
(274.3 m) or less from the shoreline in
North Carolina must meet the anchoring
system and net panel weak link
requirements in paragraphs
(d)(7)(ii)(C)(1) and (d)(7)(ii)(C)(2) of this
section, or the following:
(i) The entire net string must be less
than 300 yards (274.3 m) from shore.
(ii) The breaking strength of each
weak link must not exceed 600 lb (272.2
kg). The weak link requirements apply
to all variations in panel size.
(iii) All net panels in a string must
contain weak links that meet one of the
following two configuration
specifications found in paragraph
(d)(6)(ii)(B)(1) or (d)(6)(ii)(B)(2) of this
section.
(iv) Regardless of the number of net
panels, all anchored gillnets must be
secured at the offshore end of the net
string with a burying anchor (an anchor
that holds to the ocean bottom through
the use of a fluke, spade, plow, or pick)
having a holding capacity equal to or
greater than an 8-lb (3.6-kg) Danforthstyle anchor, and at the inshore end of
the net string with a dead weight equal
to or greater than 31 lb (14.1 kg).
(D) Groundlines. On or before October
6, 2008, all groundlines must be
comprised entirely of sinking and/or
neutrally buoyant line unless exempted
from this requirement under paragraph
(a)(4). The attachment of buoys, toggles,
or other floatation devices to
groundlines is prohibited.
(8) [Reserved]
(e) Restrictions applicable to drift
gillnet gear—(1) Cape Cod Bay
Restricted Area—(i) Area. The Cape Cod
Bay Restricted Area consists of the Cape
Cod Bay right whale critical habitat area
specified under 50 CFR 226.203(b),
unless the Assistant Administrator
changes that area in accordance with
paragraph (i) of this section.
(ii) Closure during the winter
restricted period—(A) Winter restricted
period. The winter restricted period for
this area is from January 1 through May
15 of each year, unless the Assistant
Administrator changes that period in
accordance with paragraph (i) of this
section.
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
(B) Closure. During the winter
restricted period, no person or vessel
may fish with or possess drift gillnet
gear in the Cape Cod Bay Restricted
Area unless the Assistant Administrator
specifies gear restrictions or alternative
fishing practices in accordance with
paragraph (i) of this section and the gear
or practices comply with those
specifications, or unless the gear is
stowed as specified in §229.2. The
Assistant Administrator may waive this
closure for the remaining portion of the
winter restricted period in any year
through a notification in the Federal
Register if NMFS determines that right
whales have left the restricted area and
are unlikely to return for the remainder
of the season.
(iii) Area-specific gear or vessel
requirements for the other restricted
period—(A) Other restricted period. The
other restricted period for the Cape Cod
Bay Restricted Area is from May 16
through December 31 of each year
unless the Assistant Administrator
changes that period in accordance with
paragraph (i) of this section.
(B) Area specific gear or vessel
requirements. During the other
restricted period, no person or vessel
may fish with or possess drift gillnet
gear in the Cape Cod Bay Restricted
Area unless that gear complies with the
gear marking requirements specified in
paragraph (b) of this section, or unless
the gear is stowed as specified in §
229.2. Additionally, no person or vessel
may fish with or possess drift gillnet
gear at night in the Cape Cod Bay
Restricted Area during the other
restricted period unless that gear is
tended, or unless the gear is stowed as
specified in § 229.2. During that time,
all drift gillnet gear set by that vessel in
the Cape Cod Bay Restricted Area must
be removed from the water and stowed
on board the vessel before a vessel
returns to port. The Assistant
Administrator may revise these
requirements in accordance with
paragraph (i) of this section.
(2) Great South Channel Restricted
Gillnet Area—(i) Area. The Great South
Channel Restricted Gillnet Area consists
of the area bounded by lines connecting
the following four points: 41°02.2′ N.
lat./69°02′ W. long., 41°43.5′ N. lat./
69°36.3′ W. long., 42°10′ N. lat./68°31′
W. long., and 41°38′ N. lat./68°13′ W.
long. This area includes most of the
Great South Channel right whale critical
habitat area specified under 50 CFR
226.203(a), with the exception of the
sliver along the western boundary
described in paragraph (e)(3)(i) of this
section. The Assistant Administrator
may change that area in accordance
with paragraph (i) of this section.
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(ii) Closure during the spring
restricted period—(A) Spring restricted
period. The spring restricted period for
the Great South Channel Restricted
Gillnet Area is from April 1 through
June 30 of each year unless the Assistant
Administrator changes that period in
accordance with paragraph (i) of this
section.
(B) Closure. During the spring
restricted period, no person or vessel
may set, fish with or possess drift gillnet
gear in the Great South Channel
Restricted Gillnet Area unless the
Assistant Administrator specifies gear
restrictions or alternative fishing
practices in accordance with paragraph
(i) of this section and the gear or
practices comply with those
specifications, or unless the gear is
stowed as specified in § 229.2.
(iii) Area-specific gear or vessel
requirements for the other restricted
period—(A) Other restricted period. The
other restricted period for the Great
South Channel Restricted Gillnet Area is
from July 1 though March 31 of each
year unless the Assistant Administrator
changes that period in accordance with
paragraph (i) of this section.
(B) Area-specific gear or vessel
requirements. During the other
restricted period, no person or vessel
may fish with or possess drift gillnet
gear in the Great South Channel
Restricted Gillnet Area unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, or unless the gear is
stowed as specified in § 229.2.
Additionally, no person or vessel may
fish with or possess drift gillnet gear at
night in the Great South Channel
Restricted Gillnet Area unless that gear
is tended, or unless the gear is stowed
as specified in § 229.2. During that time,
all drift gillnet gear set by that vessel in
the Great South Channel Restricted
Gillnet Area must be removed from the
water and stowed on board the vessel
before a vessel returns to port. The
Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(3) Great South Channel Sliver
Restricted Area—(i) Area. The Great
South Channel Sliver Restricted Area
consists of the area bounded by lines
connecting the following points:
41°02.2′ N. lat./69°02′ W. long., 41°43.5′
N. lat./69°36.3′ W. long., 41°40′ N. lat./
69°45′ W. long., and 41°00′ N. lat./
69°05′ W. long. The Assistant
Administrator may change that area in
accordance with paragraph (i) of this
section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess drift gillnet
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gear in the Great South Channel Sliver
Restricted Gillnet Area unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, or unless the gear is
stowed as specified in § 229.2.
Additionally, no person or vessel may
fish with or possess drift gillnet gear at
night in the Great South Channel Sliver
Restricted Area unless that gear is
tended, or unless the gear is stowed as
specified in § 229.2. During that time,
all drift gillnet gear set by that vessel in
the Great South Channel Sliver
Restricted Area must be removed from
the water and stowed on board the
vessel before a vessel returns to port.
The Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(4) Stellwagen Bank/Jeffreys Ledge
Restricted Area—(i) Area. The
Stellwagen Bank/Jeffreys Ledge
Restricted Area includes all Federal
waters of the Gulf of Maine, except
those designated as right whale critical
habitat under 50 CFR 226.203(b), that lie
south of 43°15′ N. lat. and west of 70°00′
W. long. The Assistant Administrator
may change that area in accordance
with paragraph (i) of this section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess drift gillnet
gear in the Stellwagen Bank/Jeffreys
Ledge Restricted Area unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, or unless the gear is
stowed as specified in § 229.2.
Additionally, no person or vessel may
fish with or possess drift gillnet gear at
night in the Stellwagen Bank/Jeffreys
Ledge Area unless that gear is tended,
or unless the gear is stowed as specified
in § 229.2. During that time, all drift
gillnet gear set by that vessel in the
Stellwagen Bank/Jeffreys Ledge
Restricted Area must be removed from
the water and stowed on board the
vessel before a vessel returns to port.
The Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(5) Other Northeast Gillnet Waters
Area—(i) Area. The Other Northeast
Gillnet Waters Area consists of all U.S.
waters from the U.S./Canada border to
Long Island, NY, at 72°30′ W. long.
south to 36°33.03′ N. lat. and east to the
eastern edge of the EEZ, with the
exception of the Cape Cod Bay
Restricted Area, Stellwagen Bank/
Jeffreys Ledge Restricted Area, Great
South Channel Restricted Gillnet Area,
Great South Channel Sliver Restricted
Area, and exempted waters listed in
paragraph (a)(3) of this section. The
Assistant Administrator may change
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
that area in accordance with paragraph
(i) of this section.
(ii) Year-round area-specific gear or
vessel requirements. No person or vessel
may fish with or possess drift gillnet
gear in the Other Northeast Gillnet
Waters Area unless that gear complies
with the gear marking requirements
specified in paragraph (b) of this
section, or unless the gear is stowed as
specified in § 229.2. Additionally, no
person or vessel may fish with or
possess drift gillnet gear at night in the
Other Northeast Gillnet Waters Area
unless that gear is tended, or unless the
gear is stowed as specified in § 229.2.
During that time, all drift gillnet gear set
by that vessel in the Other Northeast
Gillnet Waters Area must be removed
from the water and stowed on board the
vessel before a vessel returns to port.
The Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(iii) Seasonal area-specific gear or
vessel requirements. From September 1
to May 31, no person or vessel may fish
with or possess drift gillnet gear in the
Other Northeast Gillnet Waters Area
that is south of a straight line from
41°18.2′ N. lat., 71°51.5′ W. long. (Watch
Hill Point, RI) south to 40°00′ N. lat. and
then east to the eastern edge of the EEZ,
unless that gear complies with the gear
marking requirements specified in
paragraph (b) of this section, or unless
the gear is stowed as specified in
§§229.2. Additionally, no person or
vessel may fish with or possess drift
gillnet gear at night in the Other
Northeast Gillnet Waters Area unless
that gear is tended, or unless the gear is
stowed as specified in § 229.2. During
that time, all drift gillnet gear set by that
vessel in the Other Northeast Gillnet
Waters Area must be removed from the
water and stowed on board the vessel
before a vessel returns to port. The
Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(6) Mid/South Atlantic Gillnet Waters
Area—(i) Area. The Mid/South Atlantic
Gillnet Waters consists of all U.S. waters
bounded on the north from Long Island,
NY at 72°30′ W. long. south to 36°33.03′
N. lat. and east to the eastern edge of the
EEZ, and bounded on the south by
32°00′ N. lat., and east to the eastern
edge of the EEZ. The Assistant
Administrator may change that area in
accordance with paragraph (i) of this
section. When the Mid/South Atlantic
Gillnet Waters Area overlaps the
Southeast U.S. Restricted Area and its
restricted period as specified in
paragraphs (f)(1) and (f)(2), then the
closure and exemption for the Southeast
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57191
U.S. Restricted Area as specified in
paragraph (f)(2) applies.
(ii) Area-specific gear or vessel
requirements. From September 1
through May 31, no person or vessel
may fish with or possess drift gillnet
gear at night in the Mid/South Atlantic
Gillnet Waters Area unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, or unless the gear is
stowed as specified in § 229.2. During
that time, no person may fish with or
possess drift gillnet gear at night in the
Mid/South Atlantic Gillnet Waters Area
unless that gear is tended, or unless the
gear is stowed as specified in § 229.2.
During that time, all drift gillnet gear set
by that vessel in the Mid/South Atlantic
Gillnet Waters Area must be removed
from the water and stowed on board the
vessel before a vessel returns to port.
The Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section. When the
Mid/South Atlantic Gillnet Waters Area
overlaps the Southeast U.S. Restricted
Area and its restricted period as
specified in paragraphs (f)(1) and (f)(2),
then the closure and exemption for the
Southeast U.S. Restricted Area as
specified in paragraph (f)(2) applies.
(7) [Reserved]
(f) Restrictions applicable to the
Southeast U.S. Restricted Area—(1)
Area. The Southeast U.S. Restricted
Area consists of the area bounded by
straight lines connecting the following
points in the order stated from south to
north, unless the Assistant
Administrator changes that area in
accordance with paragraph (i) of this
section:
Point
SERA1
SERA2
SERA3
SERA4
SERA5
SERA6
SERA7
SERA8
..................
..................
..................
..................
..................
..................
..................
..................
N. lat.
27°51′
27°51′
32°00′
32°36′
32°51′
33°15′
33°27′
(2)
W. long.
(1)
80°00′
80°00′
78°52′
78°36′
78°24′
78°04′
78°33.9′
1 Florida
2 South
shoreline.
Carolina shoreline.
(i) Southeast U.S. Restricted Area N.
The Southeast U.S. Restricted Area N
consists of the Southeast U.S. Restricted
Area from 29°00′ N. lat. northward.
(ii) Southeast U.S. Restricted Area S.
The Southeast U.S. Restricted Area S
consists of the Southeast U.S. Restricted
Area southward of 29°00′ N. lat.
(2) Restricted periods, closure, and
exemptions—(i) Restricted periods. The
restricted period for the Southeast U.S.
Restricted Area N is from November 15
through April 15, and the restricted
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period for the Southeast U.S. Restricted
Area S is from December 1 through
March 31, unless the Assistant
Administrator revises the restricted
period in accordance with paragraph (i)
of this section.
(ii) Closure for gillnets. (A) Except as
provided under paragraph (f)(2)(v) of
this section, fishing with or possessing
gillnet in the Southeast U.S. Restricted
Area N during the restricted period is
prohibited.
(B) Except as provided under
paragraph (f)(2)(iii) of this section and
(f)(2)(iv) of this section, fishing with
gillnet in the Southeast U.S. Restricted
Area S during the restricted period is
prohibited.
(iii) Exemption for Southeastern U.S.
Atlantic shark gillnet fishery. Fishing
with gillnet for sharks with webbing of
5 inches (12.7 cm) or greater stretched
mesh is exempt from the restrictions
under paragraph (f)(2)(ii)(B) if:
(A) The gillnet is deployed so that it
encloses an area of water;
(B) A valid commercial directed shark
limited access permit has been issued to
the vessel in accordance with 50 CFR
635.4(e) and is on board;
(C) No net is set at night or when
visibility is less than 500 yards (1,500 ft,
460 m);
(D) The gillnet is removed from the
water before night or immediately if
visibility decreases below 500 yards
(1,500 ft, 460 m);
(E) Each set is made under the
observation of a spotter plane;
(F) No gillnet is set within 3 nautical
miles (5.6 km) of a right, humpback, or
fin whale;
(G) The gillnet is removed
immediately from the water if a right,
humpback, or fin whale moves within 3
nautical miles (5.6 km) of the set gear;
(H) The gear complies with the gear
marking requirements specified in
paragraph (b) of this section; and
(I) The operator of the vessel calls the
Southeast Fisheries Science Center
Panama City Laboratory in Panama City,
FL, not less than 48 hours prior to
departing on any fishing trip in order to
arrange for observer coverage. If the
Panama City Laboratory requests that an
observer be taken on board a vessel
during a fishing trip at any time from
December 1 through March 31 south of
29°00′ N. lat., no person may fish with
such gillnet aboard that vessel in the
Southeast U.S. Restricted Area S unless
an observer is on board that vessel
during the trip.
(iv) Exemption for Spanish Mackerel
component of the Southeast Atlantic
gillnet fishery. Fishing with gillnet for
Spanish mackerel is exempt from the
restrictions under paragraph (f)(2)(ii)(B)
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
from December 1 through December 31,
and from March 1 through March 31 if:
(A) Gillnet mesh size is between 3.5
inches (8.9 cm) and 4 7⁄8 inches (12.4
cm) stretched mesh;
(B) A valid commercial vessel permit
for Spanish mackerel has been issued to
the vessel in accordance with 50 CFR
622.4(a)(2)(iv) and is on board;
(C) No person may fish with, set,
place in the water, or have on board a
vessel a gillnet with a float line longer
than 800 yards (2,400 ft, 732 m);
(D) No person may fish with, set, or
place in the water more than one gillnet
at any time;
(E) No more than two gillnets,
including any net in use, may be
possessed at any one time; provided,
however, that if two gillnets, including
any net in use, are possessed at any one
time, they must have stretched mesh
sizes (as allowed under the regulations)
that differ by at least .25 inch (.64 cm);
(F) No person may soak a gillnet for
more than 1 hour. The soak period
begins when the first mesh is placed in
the water and ends either when the first
mesh is retrieved back on board the
vessel or the gathering of the gillnet is
begun to facilitate retrieval on board the
vessel, whichever occurs first; providing
that, once the first mesh is retrieved or
the gathering is begun, the retrieval is
continuous until the gillnet is
completely removed from the water;
(G) No net is set at night or when
visibility is less than 500 yards (1,500 ft,
460 m);
(H) The gillnet is removed from the
water before night or immediately if
visibility decreases below 500 yards
(1,500 ft, 460 m);
(I) No net is set within 3 nautical
miles (5.6 km) of a right, humpback, or
fin whale;
(J) The gillnet is removed immediately
from the water if a right, humpback, or
fin whale moves within 3 nautical miles
(5.6 km) of the set gear; and
(K) The gear complies with the gear
marking requirements specified in
paragraph (b) of this section, the
universal anchored gillnet gear
requirements specified in paragraph
(d)(1) of this section, and the areaspecific requirements for anchored
gillnets specified in paragraphs
(d)(7)(ii)(A) through (d)(7)(ii)(D) of this
section for the Mid/South Atlantic
Gillnet Waters.
(v) Exemption for vessels in transit
with gillnet aboard. Possession of gillnet
aboard a vessel in transit is exempt from
the restrictions under paragraph
(f)(2)(ii)(A) of this section if: All nets are
covered with canvas or other similar
material and lashed or otherwise
securely fastened to the deck, rail, or
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drum; and all buoys, high flyers, and
anchors are disconnected from all
gillnets. No fish may be possessed
aboard such a vessel in transit.
(vi) [Reserved]
(g) Restrictions applicable to the
Other Southeast Gillnet Waters Area—
(1) Area. The Other Southeast Gillnet
Waters Area consists of the area from
32°00′ N. lat. (near Savannah, GA) south
to 27°51′ N. lat. for the Southeast
Atlantic gillnet fishery, and from 32°00
N. lat. south to 26°46.50′ N. lat. (near
West Palm Beach, FL) for the
Southeastern U.S. Atlantic shark gillnet
fishery, and extending from 80°00′ W.
long. east to the eastern edge of the EEZ,
for both the Southeast Atlantic gillnet
and Southeastern U.S. Atlantic gillnet
fisheries unless the Assistant
Administrator changes this area in
accordance with paragraph (i) of this
section.
(2) Restrictions for Southeastern U.S.
Atlantic shark gillnet fishery. No person
or vessel may fish with or possess
gillnet gear for shark with webbing of 5
inches (12.7 cm) or greater stretched
mesh in the Other Southeast Gillnet
Waters Area north of 29°00′ N. lat. (near
New Smyrna Beach, FL) from November
15 through April 15 and south of 29°00′
N. lat. from December 1 through March
31 unless that gear complies with the
gear marking requirements specified in
paragraph (b) of this section, and the set
restrictions listed below, or unless the
gear is stowed as specified in § 229.2.
The Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(i) Set restrictions. All gillnets must
comply with the following set
restrictions:
(A) No net is set within 3 nautical
miles (5.6 km) of a right, humpback, or
fin whale; and
(B) If a right, humpback, or fin whale
moves within 3 nautical miles (5.6 km)
of the set gear, the gear is removed
immediately from the water.
(3) Restrictions for Southeast Atlantic
gillnet fishery. No person or vessel may
fish with or possess gillnet gear in the
Other Southeast Gillnet Waters Area,
except as provided in paragraph (g)(2) of
this section, north of 29°00′ N. lat. from
November 15 through April 15 and
south of 29°00′ N. lat. from December 1
through March 31 unless that gear
complies with the gear marking
requirements specified in paragraph (b)
of this section, the universal anchored
gillnet gear requirements specified in
paragraph (d)(1) of this section, and the
area-specific requirements for anchored
gillnets specified in paragraphs
(d)(7)(ii)(A) through (d)(7)(ii)(D) of this
section for the Mid/South Atlantic
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Gillnet Waters, or unless the gear is
stowed as specified in § 229.2. The
Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(4) [Reserved]
(h) Restrictions applicable to the
Southeast U.S. Monitoring Area—(1)
Area. The Southeast U.S. Monitoring
Area consists of the area from 27°51′ N.
lat. (near Sebastian Inlet, FL) south to
26°46.50′ N. lat. (near West Palm Beach,
FL), extending from the shoreline or
exemption line out to 80°00′ W. long.,
unless the Assistant Administrator
changes that area in accordance with
paragraph (i) of this section.
(2) Restrictions for Southeastern U.S.
Atlantic shark gillnet fishery. No person
or vessel may fish with or possess
gillnet gear for shark with webbing of 5
inches (12.7 cm) or greater stretched
mesh in the Southeast U.S. Monitoring
Area from December 1 through March
31 unless that gear complies with the
gear marking requirements specified in
paragraph (b) of this section, or unless
the gear is stowed as specified in
§ 229.2, and the person or vessel
satisfies the vessel monitoring system
and observer requirements listed below.
The Assistant Administrator may revise
these requirements in accordance with
paragraph (i) of this section.
(i) Vessel monitoring systems. No
person or vessel may fish with or
possess gillnet gear for shark with
webbing of 5 inches (12.7 cm) or greater
stretched mesh in the Southeast U.S.
Monitoring Area during the restricted
period unless the operator of the vessel
is in compliance with the vessel
monitoring system (VMS) requirements
found in 50 CFR 635.69.
(ii) At-sea observer coverage. When
selected, vessels are required to take
observers on a mandatory basis in
compliance with the requirements for
at-sea observer coverage found in 50
CFR 229.7. Any vessel that fails to carry
an observer once selected is prohibited
from fishing pursuant to 50 CFR part
635.
(iii) [Reserved]
(i) Other provisions. In addition to
any other emergency authority under
the Marine Mammal Protection Act, the
Endangered Species Act, the MagnusonStevens Fishery Conservation and
Management Act, or other appropriate
authority, the Assistant Administrator
may take action under this section in
the following situations:
(1) Entanglements in critical habitat
or restricted areas. If a serious injury or
mortality of a right whale occurs in the
Cape Cod Bay Restricted Area from
January 1 through May 15, in the Great
South Channel Restricted Area from
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
April 1 through June 30, the Southeast
U.S. Restricted Area N from November
15 to April 15, or the Southeast U.S.
Restricted Area S from December 1
through March 31 as the result of an
entanglement by trap/pot or gillnet gear
allowed to be used in those areas and
times, the Assistant Administrator shall
close that area to that gear type (i.e.,
trap/pot or gillnet) for the rest of that
time period and for that same time
period in each subsequent year, unless
the Assistant Administrator revises the
restricted period in accordance with
paragraph (i)(2) of this section or unless
other measures are implemented under
paragraph (i)(2) of this section.
(2) Other special measures. The
Assistant Administrator may revise the
requirements of this section through a
publication in the Federal Register if:
(i) NMFS verifies that certain gear
characteristics are both operationally
effective and reduce serious injuries and
mortalities of endangered whales;
(ii) New gear technology is developed
and determined to be appropriate;
(iii) Revised breaking strengths are
determined to be appropriate;
(iv) New marking systems are
developed and determined to be
appropriate;
(v) NMFS determines that right
whales are remaining longer than
expected in a closed area or have left
earlier than expected;
(vi) NMFS determines that the
boundaries of a closed area are not
appropriate;
(vii) Gear testing operations are
considered appropriate; or
(viii) Similar situations occur.
(3) Seasonal Area Management (SAM)
Program. Until October 6, 2008, in
addition to existing requirements for
vessels deploying anchored gillnet or
trap/pot gear in the Other Northeast
Gillnet Waters, Northern Inshore State
Trap/Pot Waters, Trap/Pot Waters,
Offshore Trap/Pot Waters, Great South
Channel Restricted Gillnet Area (July 1
through July 31), Great South Channel
Sliver Restricted Area (May 1 through
July 31), Great South Channel Restricted
Trap/Pot Area (July 1 through July 31),
and Stellwagen Bank/Jeffreys Ledge
Restricted Area (anchored gillnet and
trap/pot area) found at § 229.32 (b)–(d),
a vessel may fish in the SAM Areas as
described in paragraphs (i)(3)(i)(A) and
(i)(3)(ii)(A) of this section, which
overlay the previously mentioned areas,
provided the gear or vessel complies
with the requirements specified in
paragraphs (i)(3)(i)(B) and (i)(3)(ii)(B) of
this section during the times specified
in those paragraphs. These requirements
are in addition to requirements found in
§ 229.32 (b)–(d). The requirements in
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57193
(i)(3)(i)(B) and (i)(3)(ii)(B) of this section
supercede requirements found at
§ 229.32 (b)–(d) when the former are
more restrictive than the latter. For
example, the closures applicable to trap/
pot and gillnet gear in the Great South
Channel found in paragraphs (c)(3)(ii)
and (d)(3)(ii) of this section are more
restrictive than the gear modifications
described in this section and, therefore,
supercede them. A copy of a chart
depicting these areas is available upon
request from the Regional
Administrator, NMFS, Northeast
Region, 1 Blackburn Drive, Gloucester,
MA 01930.
(i) SAM West—(A) Area. SAM West
consists of all waters bounded by
straight lines connecting the following
points in the order stated:
SAM WEST
Point
N. lat.
W. long
1W .........................
42°30′
70°30′
2W .........................
42°30′
69°24′
3W .........................
41°48.9′
69°24′
4W .........................
41°40′
69°45′
5W .........................
41°40′
69°57′
and along the eastern shoreline of Cape Cod
to
6W .........................
42°04.8′
70°10′
7W .........................
42°12′
70°15′
8W .........................
42°12′
70°30′
(B) Gear or vessel requirements.
Unless otherwise authorized by the
Assistant Administrator, in accordance
with paragraph (i)(2) of this section,
from March 1 through April 30, no
person or vessel may fish with or
possess anchored gillnet or trap/pot gear
in SAM West unless that gear complies
with the following gear modifications,
or unless the gear is stowed as specified
in § 229.2.
(1) Anchored gillnet gear—(i)
Groundlines. All groundlines must be
made entirely of sinking and/or
neutrally buoyant line. Floating
groundlines are prohibited. The
attachment of buoys, toggles, or other
floatation devices to groundlines is
prohibited.
(ii) Buoy lines. All buoy lines must be
composed of sinking line except the
bottom portion of the line, which may
be a section of floating line not to
exceed one-third the overall length of
the buoy line.
(iii) Buoy line weak links. All buoys,
flotation devices and/or weights (except
gillnets, anchors, and leadline woven
into the buoy line), such as surface
buoys, high flyers, sub-surface buoys,
toggles, window weights, etc., must be
attached to the buoy line with a weak
link placed as close to each individual
buoy, flotation device and/or weight as
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operationally feasible that has a
maximum breaking strength of 1,100 lb
(499.0 kg). The weak link must be
chosen from the following list approved
by NMFS: Swivels, plastic weak links,
rope of appropriate breaking strength,
hog rings, rope stapled to a buoy stick,
or other materials or devices approved
in writing by the Assistant
Administrator. Weak links must break
cleanly leaving behind the bitter end of
the line. The bitter end of the line must
be free of any knots when the weak link
breaks. Splices are not considered to be
knots for the purposes of this provision.
A brochure illustrating the techniques
for making weak links is available from
the Regional Administrator, NMFS,
Northeast Region upon request.
(iv) Net panel weak links. The
breaking strength of each weak link
must not exceed 1,100 lb (499.0 kg). The
weak link requirements apply to all
variations in panel size. All net panels
in a string must contain weak links that
meet one of the following two
configuration specifications found in
paragraph (d)(6)(ii)(B)(1) or
(d)(6)(ii)(B)(2) of this section.
(v) Anchoring systems. All anchored
gillnets, regardless of the number of net
panels, must be secured at each end of
the net string with a burying anchor (an
anchor that holds to the ocean bottom
through the use of a fluke, spade, plow,
or pick) having the holding capacity
equal to or greater than a 22-lb (10.0-kg)
Danforth-style anchor. Dead weights do
not meet this requirement. A brochure
illustrating the techniques for rigging
anchoring systems is available from the
Regional Administrator, NMFS,
Northeast Region upon request.
(2) Trap/pot gear—(i) Groundlines.
All groundlines must be made entirely
of sinking and/or neutrally buoyant line.
Floating groundlines are prohibited. The
attachment of buoys, toggles, or other
floatation devices to groundlines is
prohibited.
(ii) Buoy lines. All buoy lines must be
composed of sinking line except the
bottom portion of the line, which may
be a section of floating line not to
exceed one-third the overall length of
the buoy line.
(iii) Northern Inshore State Trap/Pot
Waters, Northern Nearshore Trap/Pot
Waters Areas, Stellwagen Bank/Jeffreys
Ledge Restricted Area, and Great South
Channel Restricted Trap/Pot Area (that
overlaps with LMA 2 and Outer Cape
LMA only) buoy line weak links. All
buoys, flotation devices, and/or weights
VerDate Aug<31>2005
15:40 Oct 04, 2007
Jkt 214001
(except traps/pots, anchors, and leadline
woven into the buoy line), such as
surface buoys, high flyers, sub-surface
buoys, toggles, window weights, etc.,
must be attached to the buoy line with
a weak link placed as close to each
individual buoy, flotation device, and/
or weight as operationally feasible that
has a maximum breaking strength of up
to 600 lb (272.2 kg). The weak link must
be chosen from the following list
approved by NMFS: Swivels, plastic
weak links, rope of appropriate breaking
strength, hog rings, rope stapled to a
buoy stick, or other materials or devices
approved in writing by the Assistant
Administrator. Weak links must break
cleanly leaving behind the bitter end of
the line. The bitter end of the line must
be free of any knots when the weak link
breaks. Splices are not considered to be
knots for the purposes of this provision.
A brochure illustrating the techniques
for making weak links is available from
the Regional Administrator, NMFS,
Northeast Region upon request.
(iv) Offshore Trap/Pot Waters Area
and Great South Channel Restricted
Trap/Pot Area (that overlaps with LMA
2/3 Overlap and LMA 3 only) buoy line
weak links. All buoys, flotation devices,
and/or weights (except traps/pots,
anchors, and leadline woven into the
buoy line), such as surface buoys, high
flyers, sub-surface buoys, toggles,
window weights, etc., must be attached
to the buoy line with a weak link placed
as close to each individual buoy,
flotation device, and/or weight as
operationally feasible that has a
maximum breaking strength of up to
1,500 lb (680.4 kg). The weak link must
be chosen from the following list
approved by NMFS: swivels, plastic
weak links, rope of appropriate breaking
strength, hog rings, rope stapled to a
buoy stick, or other materials or devices
approved in writing by the Assistant
Administrator. Weak links must break
cleanly leaving behind the bitter end of
the line. The bitter end of the line must
be free of any knots when the weak link
breaks. Splices are not considered to be
knots for the purposes of this provision.
A brochure illustrating the techniques
for making weak links is available from
the Regional Administrator, NMFS,
Northeast Region upon request.
(ii) SAM East—(A) Area. SAM East
consists of all waters bounded by
straight lines connecting the following
points in the order stated:
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SAM EAST
Point
1E
2E
3E
4E
5E
.........................
.........................
.........................
.........................
.........................
N. Lat.
W. Long.
42°30′
42°30′
42°09′
41°00′
41°40′
69°45′
67°27′
67°08.4′
69°05′
69°45′
(B) Gear or vessel requirements.
Unless otherwise authorized by the
Assistant Administrator, in accordance
with paragraph (i)(2) of this section,
from May 1 through July 31, no person
or vessel may fish with or possess
anchored gillnet or trap/pot gear in
SAM East unless that gear complies
with the gear modifications found in
paragraphs (i)(3)(i)(B)(1) and
(i)(3)(i)(B)(2) of this section, or unless
the gear is stowed as specified in
§ 229.2.
PART 635—ATLANTIC HIGHLY
MIGRATORY SPECIES
6. The authority citation for 50 CFR
part 635 continues to read as follows:
I
Authority: 16 U.S.C. 971 et seq.; 16 U.S.C.
1801 et seq.
7. In § 635.69, paragraph (a)(3) is
revised to read as follows:
I
§ 635.69
Vessel monitoring systems.
(a) * * *
(3) Whenever a vessel, issued a
directed shark LAP, is away from port
with a gillnet on board during the right
whale calving season specified in the
regulations implementing the Atlantic
Large Whale Take Reduction Plan
Regulations in § 229.32 of this title.
*
*
*
*
*
PART 648—FISHERIES OF THE
NORTHEASTERN UNITED STATES
8. The authority citation for 50 CFR
part 648 continues to read as follows:
I
Authority: 16 U.S.C. 1801 et seq.
9. In § 648.264, paragraph (a)(6)(i) is
revised to read as follows:
I
§ 648.264
Gear requirements/restrictions.
(a) * * *
(6) Additional gear requirements. (i)
Vessels must comply with the gear
regulations found at § 229.32 of this
title.
*
*
*
*
*
[FR Doc. 07–4904 Filed 10–1–07; 8:45 am]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 72, Number 193 (Friday, October 5, 2007)]
[Rules and Regulations]
[Pages 57104-57194]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 07-4904]
[[Page 57103]]
-----------------------------------------------------------------------
Part II
Department of Commerce
-----------------------------------------------------------------------
National Oceanic and Atmospheric Administration
-----------------------------------------------------------------------
50 CFR Parts 229, 635, and 648
Taking of Marine Mammals Incidental to Commercial Fishing Operations;
Atlantic Large Whale Take Reduction Plan Regulations; Final Rule
Federal Register / Vol. 72, No. 193 / Friday, October 5, 2007 / Rules
and Regulations
[[Page 57104]]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Parts 229, 635, and 648
[Docket No. 0612242977-7216-01; I.D. 120304D]
RIN 0648-AS01
Taking of Marine Mammals Incidental to Commercial Fishing
Operations; Atlantic Large Whale Take Reduction Plan Regulations
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS issues this final rule to amend the regulations
implementing the Atlantic Large Whale Take Reduction Plan (ALWTRP).
This final rule revises the management measures for reducing the
incidental mortality and serious injury to the Northern right whale
(Eubalaena glacialis), humpback whale (Megaptera novaeangliae), and fin
whale (Balaenoptera physalus) in commercial fisheries to meet the goals
of the Marine Mammal Protection Act (MMPA) and the Endangered Species
Act (ESA). The measures identified in the ALWTRP are also intended to
benefit minke whales (Balaenoptera acutorostrata), which are not
strategic, but are known to be taken incidentally in commercial
fisheries. This final rule implements additional regulations for the
fisheries currently covered by the ALWTRP (the Northeast sink gillnet,
Northeast/Mid-Atlantic American lobster trap/pot, Mid-Atlantic gillnet,
Southeast Atlantic gillnet, and Southeastern U.S. Atlantic shark
gillnet fisheries) and regulates several fisheries from the MMPA List
of Fisheries for the first time under the ALWTRP, including the
following: Northeast anchored float gillnet, Northeast drift gillnet,
Atlantic blue crab, and Atlantic mixed species trap/pot fisheries
targeting crab (red, Jonah, and rock), hagfish, finfish (black sea
bass, scup, tautog, cod, haddock, pollock, redfish (ocean perch), and
white hake), conch/whelk, and shrimp.
DATES: The amendments to Sec. Sec. 229.2, 229.3, and 648.264(a)(6)(i)
are effective April 5, 2008 and the amendment to Sec. 635.69(a)(3) is
effective November 5, 2007.
As specified in the regulatory text section of this document,
amendments to Sec. 229.32 are effective as follows:
Paragraphs (f) introductory text, (f)(2), and (f)(3) are
revised effective November 5, 2007;
Amendments to Sec. 229.32(f)(1)(iii) and
(g)(4)(i)(B)(1)(vi) are added effective November 5, 2007 to April 5,
2008;
Paragraphs (f)(1)(ii) and (g)(4)(i)(B)(1)(iii) are removed
and reserved effective November 5, 2007;
Subsequent revision of Sec. 229.32 is effective April 5,
2008 except for paragraphs (c)(5)(ii)(B), (c)(6)(ii)(B), (c)(7)(ii)(C),
(c)(8)(ii)(B), (c)(9)(ii)(B), (d)(6)(ii)(D), and (d)(7)(ii)(D), which
will be effective October 5, 2008.
ADDRESSES: Copies of the Final Environmental Impact Statement/
Regulatory Impact Review for this action can be obtained from the
ALWTRP Web site listed under the Electronic Access portion of this
document. Atlantic Large Whale Take Reduction Team (ALWTRT) meeting
summaries, progress reports on implementation of the ALWTRP, and the
small entity compliance guide may be obtained by writing Diane
Borggaard, NMFS, Northeast Region, 1 Blackburn Drive, Gloucester, MA
01930. For additional ADDRESSES and Web sites for document availability
see SUPPLEMENTARY INFORMATION section.
Written comments regarding the burden-hour estimates or other
aspects of the collection-of-information requirements contained in this
final rule may be submitted to Mary Colligan, Assistant Regional
Administrator for Protected Resources, National Marine Fisheries
Service, Northeast Region, 1 Blackburn Drive, Gloucester, MA 01930 and
by e-mail to David--Rostker@omb.eop.gov, or fax to 202-395-7285.
FOR FURTHER INFORMATION CONTACT: Diane Borggaard, NMFS, Northeast
Region, 978-281-9300 Ext. 6503, diane.borggaard@noaa.gov; Kristy Long,
NMFS, Office of Protected Resources, 301-713-2322,
kristy.long@noaa.gov; or Barb Zoodsma, NMFS, Southeast Region, 904-321-
2806, barb.zoodsma@noaa.gov.
SUPPLEMENTARY INFORMATION:
Electronic Access
Several of the background documents for the ALWTRP and the take
reduction planning process can be downloaded from the ALWTRP Web site
at https://www.nero.noaa.gov/whaletrp/. Copies of the most recent marine
mammal stock assessment reports may be obtained by writing to Dr.
Richard Merrick, NMFS, 166 Water Street, Woods Hole, MA 02543 or can be
downloaded from the Internet at https://www.nefsc.noaa.gov/psb/
assesspdfs.htm. The complete text of the regulations implementing the
ALWTRP can be found either in the Code of Federal Regulations (CFR) at
50 CFR 229.32 or downloaded from the Web site, along with a guide to
the regulations.
Background
This final rule implements modifications to the ALWTRP as suggested
by the ALWTRT, as well as modifications deemed necessary by NMFS to
meet the goals of the MMPA and ESA. Details concerning the development
and justification of this final rule were provided in the preamble to
the proposed rule (70 FR 35894, June 21, 2005) and are not repeated
here. This final rule also incorporates a recent amendment to the
ALWTRP (72 FR 34632, June 25, 2007) that implemented, with revisions,
previous ALWTRP regulations by expanding the Southeast U.S. Restricted
Area to include waters within 35 nm (64.82 km) of the South Carolina
coast, dividing the Southeast U.S. Restricted Area into Southeast U.S.
Restricted Areas North and South, and modified regulations pertaining
to gillnetting within the Southeast U.S. Restricted Area.
Changes to the Boundaries and Seasons
The ALWTRP gear modifications for regulated areas of the east coast
will extend out to the eastern edge of the exclusive economic zone
(EEZ) (effective April 7, 2008) (See Figures 1 and 2). The ALWTRP will
also modify seasonal requirements along the east coast (effective April
7, 2008). Broad-based gear modifications will be required on a year-
round basis from Maine to 41[deg]18.2' N. lat. and 71[deg]51.5' W.
long. (Watch Hill, RI), south to 40[deg]00' N. lat., and east to the
eastern edge of the EEZ. NMFS will require gear modifications in the
Mid and South Atlantic (called ``Mid/South Atlantic'' from this point)
on a seasonal basis, from September 1 to May 31, when more sightings
are reported and the risk of entanglement with commercial fishing gear
is greater. Under this final rule, a line drawn from 41[deg]18.2' N.
lat. and 71[deg]51.5' W. long. (Watch Hill, RI), south to 40[deg]00' N.
lat., and east to the eastern edge of the EEZ, will serve as the
northern boundary for seasonal gear modifications in the Mid/South
Atlantic and 32[deg]00' N. lat. (near Savannah, GA) east to the eastern
edge of the EEZ will serve as the southern boundary. Portions of the
Mid/South Atlantic Gillnet Waters (i.e., waters within 35 nm (64.82 km)
of the South Carolina coast) will be included in the Southeast U.S.
Restricted Area (a gillnet management area) during the restricted
periods associated with the right whale calving season (i.e. November
15 to April 15).
[[Page 57105]]
NMFS is revising the seasons and boundaries for the southeast from
November 15 to April 15 for all ALWTRP regulated fisheries, except for
the gillnet fisheries modified through the recent amendment to the
ALWTRP (72 FR 34632, June 25, 2007), between 32[deg]00' N. lat. (near
Savannah, GA) and 29[deg]00' N. lat. (near New Smyrna Beach, FL) east
to the eastern edge of the EEZ. From December 1 to March 31,
restrictions will be required for the Atlantic blue crab and Atlantic
mixed species trap/pot fisheries and the Southeast Atlantic gillnet
fishery between 29[deg]00' N. lat. and 27[deg]51' N. lat. (near
Sebastian Inlet, FL) east to the eastern edge of the EEZ, and for the
Southeastern U.S. Atlantic shark gillnet fishery between 29[deg]00' N.
lat. and 26[deg]46.50' N. lat. (near West Palm Beach, FL) east to the
eastern edge of the EEZ. The Southeastern U.S. shark gillnet fishery as
regulated in this final rule includes shark gillnetting with 5-inch
(12.7-cm) or greater stretched mesh south of the South Carolina/Georgia
border.
Changes to the Lobster Trap/Pot Gear Requirements
Northern Inshore State and Nearshore Trap/Pot Waters, Cape Cod Bay
Restricted Area (May 16-December 31), Stellwagen Bank/Jeffreys Ledge
Restricted Area, and Great South Channel Restricted Area (Nearshore
Portion)
The regulations for Northern Nearshore Trap/Pot Waters, Stellwagen
Bank/Jeffreys Ledge Restricted Area, and the Federal portion of the
Cape Cod Bay Restricted Area (May 16-December 31) will continue to
require one buoy line on trawls of 5 or fewer traps.
For Northern Inshore State Trap/Pot Waters and the state portion of
the Cape Cod Bay Restricted Area (May 16-December 31), this final rule
will eliminate the Lobster Take Reduction Technology List (i.e., a list
of gear modification options) and require a 600-lb (272.2-kg) weak link
on all flotation devices and/or weighted devices (except traps/pots,
anchors, and leadline woven into the buoy line) attached to the buoy
line (effective April 7, 2008).
This final rule will also lower the weak link breaking strength on
all flotation devices and/or weighted devices attached to the buoy line
in the nearshore portion of the Great South Channel Restricted Area
that overlaps with Lobster Management Area (LMA) 2 and the Outer Cape
(July 1-March 31) from 2,000 lb (907.2 kg) to 600 lb (272.2 kg)
(effective April 7, 2008). All fishermen in the nearshore portion of
the Great South Channel Restricted Area will then be required to have a
600-lb (272.2-kg) weak link on all flotation devices and/or weighted
devices (except traps/pots, anchors, and leadline woven into the buoy
line) attached to the buoy line.
Offshore Trap/Pot Waters Area and Great South Channel Restricted Area
(Offshore Portion)
This final rule will extend the southern boundary of the Offshore
Trap/Pot Waters Area by following the 100-fathom (600-ft or 182.9-m)
line from 35[deg]30' N. lat. (just north of Cape Hatteras, NC) to
27[deg]51' N. lat. and then extending out to the eastern edge of the
EEZ (effective April 7, 2008). In addition to the current requirements,
this final rule will lower the maximum breaking strength of weak links
and require weak links with appropriate breaking strength on all
flotation devices and/or weighted devices (except traps/pots, anchors,
and leadline woven into the buoy line) attached to the buoy line in
Offshore Trap/Pot Waters that overlaps with the LMA 3 (including the
area known as the Area 2/3 Overlap and Area 3/5 Overlap) and the
offshore portion of the Great South Channel Restricted Area that
overlaps with the LMA 2/3 overlap and LMA 3 Areas from 2,000 lb (907.2
kg) to 1,500 lb (680.4 kg) (effective April 7, 2008).
Southern Nearshore Trap/Pot Waters Area
This final rule will extend the southern boundary of the Southern
Nearshore Trap/Pot Waters Area by following the 100-fathom (600-ft or
182.9-m) line from 35[deg]30' N. lat. to 27[deg]51' N. lat. and then
extending the boundary inshore to the shoreline or exempted areas. The
Southern Nearshore Trap/Pot Waters is defined by LMAs 4, 5, and 6
(except for the exempted areas) north of 35[deg]30' N. lat. and by the
100-fathom (600-ft or 182.9-m) line west to the shoreline or exempted
areas south of 35[deg]30' N. lat. In addition to the current
requirements, this final rule will implement the regulations currently
required in the Southern Nearshore Trap/Pot Waters in the portion of
LMA 6 that is neither exempted under the ALWTRP waters (i.e., mouth of
Long Island Sound) nor currently regulated by the ALWTRP (effective
April 7, 2008). This final rule will also require a 600-lb (272.2-kg)
weak link on all flotation devices and/or weighted devices (except
traps/pots, anchors, and leadline woven into the buoy line) attached to
the buoy line.
Changes to the Other Trap/Pot Gear Requirements
Effective April 7, 2008, NMFS will regulate the following trap/pot
fisheries under the ALWTRP (designated as ``Other Trap/Pot
Fisheries''): Crab (red, Jonah, rock, and blue), hagfish, finfish
(black sea bass, scup, tautog, cod, haddock, pollock, redfish (ocean
perch), and white hake), conch/whelk, and shrimp. Through this final
rule, these Other Trap/Pot fisheries will be required to comply with
current ALWTRP regulations, including the universal gear modifications,
and will follow the same area designations and requirements (e.g., weak
links, Seasonal Area Management (SAM) program requirements as modified
in this final rule, and Cape Cod Bay and Great South Channel Area
restrictions) currently required and revised for the lobster trap/pot
fisheries covered by the ALWTRP. Where applicable, these fisheries will
also be regulated under the ALWTRP within the portion of LMA 6 that is
not exempted by the ALWTRP (i.e., mouth of Long Island Sound). In
addition to complying with the current ALWTRP requirements, the Other
Trap/Pot Fisheries will be required to comply with the modifications
for the lobster trap/pot fishery specified in this final rule
(effective April 7, 2008) except for the groundline requirements where
applicable as noted under the ``Broad-Based Gear Modifications''
section below.
Red Crab Trap/Pot Gear
Through this final rule, the maximum weak link breaking strength
will be lowered from 3,780 lb (1,714.6 kg) to 2,000 lb (907.2 kg). A
2,000-lb (907.2-kg) weak link will be required on all flotation devices
and/or weighted devices (except traps/pots, anchors, and leadline woven
into the buoy line) attached to the buoy line in the red crab fishery
(effective April 7, 2008).
Changes to the All Trap/Pot Gear Requirements
Broad-Based Gear Modifications
The majority of the broad-based gear modifications identified in
this final rule for trap/pot gear will become effective six months
after publication of this final rule, April 7, 2008, except for the
groundline requirement that will be phased-in and effective October 6,
2008, except in SAM and Cape Cod Bay Restricted Areas. When the
majority of the broad-based gear modifications become effective on
April 7, 2008, the Dynamic Area Management (DAM) program will be
eliminated. When the sinking/neutrally buoyant groundline
[[Page 57106]]
requirement becomes fully effective, October 6, 2008, this final rule
will eliminate the Seasonal Area Management (SAM) program. However,
until October 6, 2008, the Other Trap/Pot Fisheries will be subject to
SAM program requirements (see modifications to area and gear
requirements as noted in this final rule).
ALWTRP-Regulated Trap/Pot Waters
Due to the addition of new trap/pot fisheries, ALWTRP-Regulated
Lobster Waters will be re-designated as ALWTRP-Regulated Trap/Pot
Waters to reflect the broader application of ALWTRP requirements.
Accordingly, under the final rule, the term ``lobster trap/pot'' will
be replaced with ``trap/pot'' where it appears in the regulations
implementing the ALWTRP.
Boundaries and Seasons
Under this final rule, the areas will be created by establishing a
line that is bounded on the west by a line running from 41[deg]18.2' N.
lat. and 71[deg]51.5' W. long. (Watch Hill, RI), south to 40[deg]00' N.
lat., and east to the eastern edge of the EEZ. The gear fished in the
area north of this line will be required to incorporate current and
revised broad-based gear modifications year-round; the gear fished in
the area south of this line to 32[deg]00' N. lat. and east to the
eastern edge of the EEZ will require gear modifications from September
1 to May 31 (effective April 7, 2008). Areas south of 32[deg]00' N.
lat. will require gear modifications in the following areas and during
the following seasonal time periods: between the 32[deg]00' N. lat. and
29[deg]00' N. lat. east to the eastern edge of the EEZ from November
15-April 15; between 29[deg]00' N. lat. and 27[deg]51' N. lat. east to
the eastern edge of the EEZ from December 1 through March 31 (effective
April 7, 2008).
Sinking/Neutrally Buoyant Groundlines
Under this final rule, the lobster trap/pot fishery currently
regulated by the ALWTRP, as well as the other trap/pot fisheries added
through this final rule, will be required to use groundline composed
entirely of sinking and/or neutrally buoyant line in the applicable
areas and time periods effective twelve months after publication of
this final rule (unless otherwise required in the Cape Cod Bay
Restricted Area for trap/pots [January 1-May 15]). The sinking and/or
neutrally buoyant groundline requirement will be effective in expanded
SAM areas effective 6 months after publication of this final rule.
Based on public comments received regarding the line between traps
and anchors, and a review of the groundline definition, NMFS finds that
the definition does not cover this portion of the gear. (The groundline
definition ``with reference to trap/pot gear, means a line connecting
traps in a trap trawl, and with reference to gillnet gear, means a line
connecting a gillnet or gillnet bridle to an anchor or buoy line.'')
NMFS did not specifically seek nor receive public comment on the
groundline definition related to the line between traps and anchors,
and accordingly cannot make any adjustments to the definition at this
time. NMFS will be conducting further investigations of this gear
configuration through contact with fishermen and states to determine
how common a practice it is in trap/pot fisheries, determine the type
of line used in this portion of the gear, quantify potential risk if
floating line is used, determine any new issues that may be raised by
requiring sinking and/or neutrally buoyant line in this area of the
gear, and discuss the appropriate management response with the ALWTRT
at the next meeting.
Weak Links
Through this final rule, weak links of the appropriate breaking
strength will be required on all flotation devices and/or weighted
devices (except traps/pots, anchors, and leadline woven into the buoy
line) attached to the buoy line (effective April 7, 2008) for all
ALWTRP-regulated areas and fisheries during the time periods when
ALWTRP restrictions apply. The Other Trap/Pot Fisheries added to the
ALWTRP by this final rule will also be subject to the weak link
requirements.
Changes to the Gillnet Gear Requirements
Other Northeast Gillnet Waters, Stellwagen Bank/Jeffreys Ledge
Restricted Area, Cape Cod Bay Restricted Area (May 16-December 31),
Great South Channel Restricted Area (July 1-March 31), and Great South
Channel Sliver Restricted Area
Anchored Gillnets
Under this final rule, NMFS will require an 1,100-lb (499.0-kg)
weak link on all flotation devices and/or weighted devices (except
gillnets, anchors, and leadline woven into the buoy line) attached to
the buoy line (effective April 7, 2008). For anchored gillnets in the
Northeast sink gillnet fishery, NMFS will also require an increase in
the number of weak links per gillnet net panel from one weak link with
a maximum breaking strength of 1,100 lb (499.0 kg) to five or more weak
links with a maximum breaking strength of 1,100 lb (499.0 kg),
depending on the length of the gillnet net panel (effective April 7,
2008). The weak link requirement will apply to all variations in panel
size. For example, gillnet net panels of 50 fathoms (300 ft or 91.4 m)
or less in length, will be required to have one weak link in the
floatline at the center of the gillnet net panel. For gillnet net
panels greater than 50 fathoms (300 ft or 91.4 m), weak links will be
placed continuously along the floatline separated by a maximum distance
of 25 fathoms (150 ft or 45.7 m). For all variations in panel size, the
following weak link requirements will apply: (1) Weak links will be
placed in the center of each of the up and down lines at each end of
each gillnet net panel, and (2) one floatline weak link will be placed
as close as possible to each end of the gillnet net panel just before
the floatline meets the up and down line. Up and down line means the
line that connects the floatline and leadline at the end of each
gillnet net panel.
In addition to the above configuration for gillnet net panel weak
links, NMFS will allow the following option for all variations in panel
size: (1) Weak links will be placed in the center of each of the up and
down lines at each end of each gillnet net panel, (2) weak links will
be placed between the floatline tie loops between gillnet net panels,
and (3) weak links will be placed between the floatline tie loop and
bridle or buoy line at each end of a net string (depending on how the
gear is configured) (see Figure 3). Tie loops mean the loops on a
gillnet net panel used to connect gillnet net panels to the buoy line,
groundline, bridle, or each other. NMFS will also be allowing the
optional configuration in the current SAM areas, as well as in
established DAM zones when a gear modification option is selected
(effective November 5, 2007). See the Changes from Proposed Rule
section (6) below for further information on the rationale for this
optional configuration, as well as for allowing it in the current SAM
areas and established DAM zones.
For the above configuration options, weak links must be chosen from
the following combinations approved by NMFS: Plastic weak links or rope
of appropriate breaking strength. If rope of appropriate breaking
strength is used throughout the floatline or as the up and down line,
or if no up and down line is present, then individual weak links are
not required on the floatline or up and down line. In addition, all
anchored gillnets, regardless of the number of gillnet net panels, will
be required to be securely anchored with the holding
[[Page 57107]]
capacity equal to or greater than a 22-lb (10.0-kg) Danforth-style
anchor at each end of the net string (effective April 7, 2008). Dead
weights and heavy leadline will not be available as an optional
anchoring system. The same configuration option would be required for
all gillnet net panels in a string.
Mid/South Atlantic Gillnet Waters
Under this final rule, the Mid-Atlantic Coastal Waters Area will be
expanded and renamed to include waters currently unregulated by the
ALWTRP that include a component of the U.S. Mid-Atlantic gillnet
fishery and Southeast Atlantic gillnet fishery. Specifically, gillnet
fisheries in the waters from 72[deg]30' W. long., south to the
Virginia/North Carolina border, east to the eastern edge of the EEZ,
and extending south to 32[deg]00' N. lat. and out to the eastern edge
of the EEZ will be referred to as Mid/South Atlantic Gillnet Waters
(effective April 7, 2008). Portions of the Mid/South Atlantic Gillnet
Waters (i.e., waters within 35 nm (64.82 km) of the South Carolina
coast) are also included in the Southeast U.S. Restricted Area during
the November 15 to April 15 right whale calving season.
Anchored Gillnets
Under this final rule, all anchored gillnets in the Mid/South
Atlantic Gillnet Waters must have an 1,100-lb (499.0-kg) weak link on
all flotation devices and/or weighted devices (except gillnets,
anchors, and leadline woven into the buoy line) attached to the buoy
line (effective April 7, 2008). Additionally, if gillnets are not
returned to port with the vessel they must contain five or more weak
links depending on the length of the gillnet net panel, with a maximum
breaking strength no greater than 1,100 lb (499.0 kg) for each gillnet
net panel; and be anchored at each end with an anchor capable of the
holding capacity equal to or greater than a 22-lb (10.0-kg) Danforth-
style anchor (effective April 7, 2008). The configuration options for
gillnet net panel weak links and anchoring are similar to that
specified for anchored gillnets in the Other Northeast Gillnet Waters
section of this rule. The same configuration option would be required
for all gillnet net panels in a string. All gillnets, even if returned
to port with the vessel, must also contain one weak link with a maximum
breaking strength no greater than 1,100 lb (499.0 kg) in the center of
the floatline of each gillnet net panel up to and including 50 fathoms
(300 ft or 91.4 m) in length, or at least every 25 fathoms (150 ft or
45.7 m) along the floatline for longer panels in previously unregulated
waters (effective April 7, 2008).
Gillnets within 300 yards (900 ft or 274.3 m) of the shoreline of
North Carolina that are not returned to port with the vessel will have
an additional option for setting their gear. Gillnets set in this area
may configure their gear as follows: five or more weak links per
gillnet net panel (depending on the length of the gillnet net panel)
with a maximum breaking strength of 600 lb (272.2 kg) must be deployed,
and be anchored with the holding capacity equal to or greater than an
8-lb (3.6-kg) Danforth-style anchor on the offshore end of the net
string and with a dead weight equal to or greater than 31-lb (14.1-kg)
on the inshore end of the net string (effective April 7, 2008). The
entire net string must be set within 300 yards (900 ft or 274.3 m) of
the beach in North Carolina for this optional anchoring system and
gillnet net panel weak link configuration. This configuration is in
addition to the final configuration of five or more weak links per
gillnet net panel (depending on the length of the gillnet net panel)
with a maximum breaking strength of 1,100-lb (499.0-kg), and anchored
with the holding capacity equal to or greater than a 22-lb (10.0-kg)
Danforth-style anchor on each end of the net string. Specifics on the
configuration options for the placement of gillnet net panel weak links
can be found in the Other Northeast Gillnet Waters section of this
rule.
At this time, NMFS is not regulating gillnets that are anchored to
the beach and subsequently hauled onto the beach to retrieve the catch.
This fishing technique is known to occur on the beaches of North
Carolina. NMFS will be discussing the appropriate management measures
for this unique fishery with the ALWTRT at a future meeting. In the
meantime, NMFS will be conducting outreach and research on this fishery
to support future discussions with the ALWTRT. NMFS will be
coordinating with the North Carolina Department of Marine Fisheries to
revise the definition for beach -based gear to help ensure landings are
reported accurately for beach-based gear versus gillnets, among other
issues.
Drift Gillnets
Under this final rule, current requirements for drift gillnet gear
in Mid/South Atlantic Gillnet Waters are expanded in time and space as
noted in the Boundaries and Seasons section above (effective April 7,
2008).
Other Southeast Gillnet Waters
Under this final rule, the management area for the Southeast
Atlantic gillnet and Southeastern U.S. Atlantic shark gillnet fisheries
off Georgia and Florida will be expanded and renamed (effective April
7, 2008). Specifically, this final rule will define the waters east of
80[deg]00' W. long. from 32[deg]00' N. lat. south to 26[deg]46.5' N.
lat. and out to the eastern edge of the EEZ as one ALWTRP management
area named ``Other Southeast Gillnet Waters''. The expansion of this
area east to the eastern edge of the EEZ will be consistent with the
ALWTRP area boundary expansion in the Mid-Atlantic.
Under this final rule, NMFS will establish the seasonal restricted
time period in Other Southeast Gillnet Waters (effective April 7,
2008). ALWTRP regulations for the Southeast Atlantic gillnet fishery
operating in the Other Southeast Gillnet Waters between 32[deg]00' N.
lat. to 29[deg]00' N. lat. (near New Smyrna Beach, FL) will be
effective from November 15 to April 15, and between 29[deg]00' N. lat.
and 27[deg]51' N. lat. will be effective from December 1 to March 31.
For the Southeastern U.S. Atlantic shark gillnet fishery, ALWTRP
regulations in the Other Southeast Gillnet Waters between 32[deg]00' N.
lat. to 29[deg]00' N. lat. will be effective from November 15 to April
15, and between 29[deg]00' N. lat. and 26[deg]46.5' N. lat. will be
effective from December 1 to March 31.
Southeast Atlantic Gillnet Fishery
All gillnet gear in Other Southeast Gillnet Waters will be
regulated in the same manner as the Mid/South Atlantic anchored gillnet
fishery (effective April 7, 2008). The regulated waters for the
Southeast Atlantic gillnet fishery south of 32[deg]00' N. lat. to
27[deg]51' N. lat. and east from 80[deg]00' W. long. to the eastern
edge of the EEZ will be required to comply with the ALWTRP universal
gear requirements (e.g., no buoy line floating at the surface and no
wet storage of gear), as well as the following: gillnets must have all
flotation devices and/or weighted devices (except gillnets, anchors,
and leadline woven into the buoy line) attached to the buoy line with a
weak link having a maximum breaking strength no greater than 1,100 lb
(499.0 kg); and have all gillnet net panels containing weak links with
a maximum breaking strength no greater than 1,100 lb (499.0 kg) in the
center of each floatline of each 50 fathom (300 ft or 91.4m) gillnet
net panel or every 25 fathoms (150 ft or 45.7 m) for longer panels
(effective April 7, 2008).
In addition, under this final rule, all gillnets in the Other
Southeast Gillnet
[[Page 57108]]
Waters that are not returned to port with the vessel will be required
to contain five or more weak links, depending on the length of the
gillnet net panel, with a maximum breaking strength no greater than
1,100 lb (499.0 kg) for each gillnet net panel; and be anchored at each
end with an anchor with the holding capacity equal to or greater than a
22-lb (10.0-kg) Danforth-style anchor (effective April 7, 2008). The
configuration options for gillnet net panel weak links and anchoring
are similar to that specified for anchored gillnets in the Other
Northeast Gillnet Waters section of this final rule. The same
configuration option would be required for all gillnet net panels in a
string.
Southeastern U.S. Atlantic Shark Gillnet Fishery
For the Southeastern U.S. Atlantic Shark gillnet fishery operating
in Other Southeast Gillnet Waters, the following requirements will be
in effect: (1) No net is set within 3 nautical miles (5.6 km) of a
right, humpback, or fin whale; and (2) If a right, humpback, or fin
whale moves within 3 nautical miles (5.6 km) of the set gear, the gear
is removed immediately from the water (effective April 7, 2008).
Southeast U.S. Restricted Area (N and S) and Southeast U.S. Monitoring
Area
Under this final rule, the management areas for the Southeastern
U.S. Atlantic shark gillnet and Southeast Atlantic gillnet fishery
management areas will be redefined (effective April 7, 2008).
Specifically, for the Southeastern U.S. Atlantic shark gillnet fishery,
the regulated waters landward of 80[deg]00' W. long. from 27[deg]51' N.
lat. to 26[deg]46.5' N. lat. will be designated as the Southeast U.S.
Monitoring Area (rather than the Southeast U.S. Observer Area). For
both the Southeastern U.S. Atlantic shark gillnet and Southeast
Atlantic gillnet fisheries, the regulated waters landward of 80[deg]00'
W. long. from 32[deg]00' N. lat. to 27[deg]51' N. lat. will be
designated as the Southeast U.S. Restricted Area, consisting of a
northern area ``N'' between 32[deg]00' N. lat. and 29[deg]00' N. lat.
and a southern area ``S'' between 29[deg]00' N. lat. and 27[deg]51' N.
lat.
Under this final rule, the management areas for gillnet fisheries
will be regulated with rolling restrictions (effective April 7, 2008).
The Southeastern U.S. Atlantic shark gillnet and Southeast Atlantic
gillnet fisheries will be regulated in waters from 32[deg]00' N. lat.
to 29[deg]00' N. lat. (near New Smyrna Beach, FL) from November 15
through April 15. The Southeastern U.S. Atlantic shark gillnet fishery
will be regulated in waters from 29[deg]00' N. lat. to 26[deg]46.5' N.
from December 1 through March 31, and the Southeast Atlantic gillnet
fishery will be regulated in waters from 29[deg]00' N. lat. to
27[deg]51' N. lat. from December 1 through March 31.
NMFS is also allowing the use of vessel monitoring system (VMS) in
lieu of the 100-percent observer coverage requirement for the
Southeastern U.S. Atlantic shark gillnets in the newly defined
Southeast U.S. Monitoring Area (27[deg]51' N. lat. to 26[deg]46.5' N.)
under the ALWTRP (effective November 5, 2007). Although 100-percent
observer coverage will no longer be required in this area, NMFS will
retain observer coverage sufficient to produce statistically reliable
results for evaluating the impact of the fishery on protected
resources. In light of the revised change from 100-percent observer
coverage to VMS, NMFS is changing the name of the ``Southeast U.S.
Observer Area'' to the ``Southeast U.S. Monitoring Area.''
Amendment 1 to the FMP for Atlantic Tunas, Swordfish, and Sharks
(68 FR 74746, December 24, 2003; 69 FR 19979, April 15, 2004; and 69 FR
28106, May 18, 2004) requires gillnet vessels issued directed shark
limited access permits that have gillnet gear on board, regardless of
their location, to employ a NMFS approved VMS during the right whale
calving season specified in the ALWTRP regulations. Currently, as
stated in the August 17, 2004, final rule (69 FR 51010, August 17,
2004) specifying November 15, 2004, as the effective date of this
requirement, the applicable right whale calving season is identified as
November 15 through March 31. This final rule will change the right
whale season specified in those regulations for the Southeast U.S.
Monitoring Area to December 1 through March 31 and amend the regulatory
text in 50 CFR 635.69(a)(3) regarding the Highly Migratory Species
(HMS) VMS requirement for Southeastern U.S. Atlantic shark gillnet
vessels.
Changes to the Other Gillnet Gear Requirements
Northeast Anchored Float Gillnet Fishery
This final rule will regulate the Northeast anchored float gillnet
fishery (gillnets anchored to the ocean floor with lines running from
the anchors to the nets at the surface) according to the requirements
for the Northeast anchored gillnet fishery requirements (effective
April 7, 2008). The Northeast anchored float gillnet fishery will be
subject to the SAM program as modified in this final rule until twelve
months after publication of this final rule, and to seasonal closures
in right whale restricted areas. Specifically, fishermen using
Northeast anchored float gillnets will be prohibited from fishing
inside the Cape Cod Bay Restricted Area annually from January 1 through
May 15, and inside the Great South Channel Restricted Area annually
from April 1 through June 30.
Northeast Drift Gillnet Fishery
This final rule will regulate the Northeast drift gillnet fishery
(i.e., nets that are present at the ocean surface and are not anchored
to the ocean floor on either end) according to the requirements for the
Mid-Atlantic drift gillnet fishery (effective April 7, 2008). The
Northeast drift gillnet fishery will not be subject to the SAM program,
but drift gillnets will be prohibited from Cape Cod Bay Restricted Area
from January 1 through May 15 and from the Great South Channel
Restricted Area from April 1 through June 30 (similar to the
requirements for anchored gillnet), except for the Sliver Area, where
restricted drift gillnet fishing will be allowed.
Changes to the All Gillnet Gear Requirements
Broad-Based Gear Modifications
Most of the broad-based gear modifications for gillnet gear
identified in this final rule will become effective six months after
publication of this final rule, April 7, 2008, except for the
groundline requirement discussed below, which will be phased-in and
effective twelve months after publication of this final rule (except in
SAM areas), October 6, 2008. When the majority of the broad-based gear
modifications become effective on April 7, 2008, the DAM program will
be eliminated. When the sinking/neutrally buoyant groundline
requirement becomes fully effective, October 6, 2008, this final rule
will eliminate the SAM program. However, until this occurs, some of the
other gillnet fisheries that will be added to the ALWTRP will be
subject to the SAM program (see modifications to area and gear
requirements as noted in this final rule).
Boundaries and Seasons
Under this final rule, an area bounded on the west by a line
running from 41[deg]18.2' N. lat. and 71[deg]51.5' W. long. (Watch
Hill, RI), south to 40[deg]00' N. lat., and east to the eastern edge of
the EEZ will be created. The gillnet gear fished in the area north of
this line will be required to incorporate current and revised broad-
based gear modifications year-round. Gillnet gear fished in the
[[Page 57109]]
area south of this line to 32[deg]00' N. lat. and east to the eastern
edge of the EEZ will be required to comply with the broad-based gear
modifications detailed above in Mid/South Atlantic Gillnet Waters from
September 1 to May 31. However, portions of the Mid/South Atlantic
Gillnet Waters (i.e., waters within 35 nm (64.82 km) of the South
Carolina coast) will be included in the Southeast U.S. Restricted Area
during the November 15 to April 15 right whale calving season. Gillnet
fishing in the area south of 32[deg]00' N. lat. will be required to
comply with the broad-based gear modifications in the following areas
and seasonal time periods: All gillnet fisheries (Southeast Atlantic
and Southeastern U.S. Atlantic shark) between 32[deg]00' N. lat. and
29[deg]00' N. lat. from November 15-April 15; Southeast Atlantic
gillnet fishery between 29[deg]00' N. lat. and 27[deg]51' N. lat. east
to the eastern edge of the EEZ from December 1-March 31; and
Southeastern U.S. Atlantic shark gillnet fisheries between 29[deg]00'
N. lat. and 26[deg]46.5' N. lat. east to the eastern edge of the EEZ
from December 1-March 31.
Sinking/Neutrally Buoyant Groundlines
Under this final rule, the Northeast anchored gillnet, Mid-Atlantic
anchored gillnet, and Southeast Atlantic gillnet fisheries currently
regulated by the ALWTRP, and the Northeast anchored float gillnet
fishery, which will be added by this final rule, will be required to
use groundline composed entirely of sinking and/or neutrally buoyant
line in the areas and time periods covered under the ALWTRP effective
on October 6, 2008. The sinking and/or neutrally buoyant groundline
requirement will be effective in expanded SAM areas effective on April
7, 2008.
Weak Links
Under this final rule, to further reduce the risk of serious injury
and mortality from entanglement in gillnet gear, weak links having a
maximum breaking strength of 1,100 lb (499.0 kg) will be required on
all flotation devices and/or weighted devices (except gillnets,
anchors, and leadline woven into the buoy line) attached to the buoy
line (effective April 7, 2008). This requirement will apply to all
current and revised ALWTRP regulated areas and gillnet fisheries. The
weak link requirement is intended to reduce the risk of entanglement
and serious injury or mortality due to entanglements in buoy lines and
surface systems.
Revised SAM Program
The final rule will amend the SAM program by establishing new
boundaries for the SAM areas and revising the gear modifications
required for fishing within these areas. The changes to the SAM program
described in this final rule will become effective on April 7, 2008, to
protect right whales. The SAM program will be eliminated October 6,
2008, when all of the broad-based gear modifications are effective.
This final rule will modify the existing coordinates for the SAM
areas. Specifically, the western boundary of SAM West will be extended
westward to encompass seasonal aggregations of right whales that occur
north of the Cape Cod Bay Restricted Area. Similarly, the southern
boundary of SAM West will be extended further south, adjoining the
Great South Channel Restricted Sliver Area, to encompass seasonal
aggregations of right whales that occur south of the current SAM West
and west of the Great South Channel Restricted Area. Finally, the
southern boundary of SAM East would be revised to include the Great
South Channel Restricted Area including the Sliver Area, but will
exclude the southeast corner of the existing SAM East area where there
have been very few right whale sightings. The western boundary of SAM
East will be extended west to 69[deg] 45'W. long. to encompass right
whales that might remain in SAM West in May (after the SAM West area
restrictions have expired) (Table 1; Figure 8).
Table 1.--Seasonal Area Management
----------------------------------------------------------------------------------------------------------------
Point Latitude (North) Longitude (West)
----------------------------------------------------------------------------------------------------------------
SAM West Polygon--in Effect From March 1-April 30
----------------------------------------------------------------------------------------------------------------
1W........................................... 42[deg]30'...................... 70[deg]30' (NW Corner)
2W........................................... 42[deg]30'...................... 69[deg]24'
3W........................................... 41[deg]48.9'.................... 69[deg]24'
4W........................................... 41[deg]40'...................... 69[deg]45'
5W........................................... 41[deg]40'...................... 69[deg]57' along the eastern
shoreline of Cape Cod to
6W........................................... 42[deg]04.8'.................... 70[deg]10'
7W........................................... 42[deg]12'...................... 70[deg]15'
8W........................................... 42[deg]12'...................... 70[deg]30'
1W........................................... 42[deg]30'...................... 70[deg]30' (NW Corner)
----------------------------------------------------------------------------------------------------------------
SAM East Polygon--in Effect From May 1-July 31
----------------------------------------------------------------------------------------------------------------
1E........................................... 42[deg]30'...................... 69[deg]45' (NW Corner)
2E........................................... 42[deg]30'...................... 67[deg]27'
3E........................................... 42[deg]09'...................... 67[deg]08.4'
4E........................................... 41[deg]00'...................... 69[deg]05'
5E........................................... 41[deg]40'...................... 69[deg]45'
1E........................................... 42[deg]30'...................... 69[deg]45' (NW Corner)
----------------------------------------------------------------------------------------------------------------
Revised SAM Gear Modifications
In addition to the changes discussed above, this final rule will
revise the gear modifications required for fishing within the SAM areas
during the applicable time periods. Under this final rule, NMFS will
allow the use of two buoy lines per trap/pot trawl or per net string,
allow the use of floating line on the bottom one-third or less of the
buoy line, and allow two configuration options for gillnet net panel
weak links. The same configuration option would be required for all
gillnet net panels in a string.
Changes to the SAM Program for All Trap/Pot Gear
Under this final rule, in addition to the measures revised for
trap/pot fisheries, the following requirements specific to the SAM and
DAM programs would apply. The SAM areas will be
[[Page 57110]]
expanded and all lobster trap/pot fisheries operating within these
areas during the restricted time periods would be subject to the
current SAM restrictions, plus the following: A second buoy line will
be allowed and the bottom one-third of the buoy line may consist of
floating line. In addition, the trap/pot fisheries subject to the SAM
program will be expanded to include: hagfish, finfish (black sea bass,
scup, tautog, cod, haddock, pollock redfish, and white hake), conch/
whelk, shrimp, red, blue, rock, and Jonah crab. The expanded SAM area
will include the Great South Channel Restricted Area; therefore, trap/
pot gear will be subject to the SAM program inside right whale
restricted areas during time periods when the requirements for fishing
inside these areas are no more conservative than the surrounding waters
(i.e., when the protections of right whale restricted areas disappear).
However, the more restrictive Great South Channel Restricted Trap/Pot
Area closure (April 1 through June 30) will supercede the SAM program.
As a result, gear modifications for fishing with trap/pot gear in the
SAM area will apply in the Great South Channel Restricted Trap/Pot Area
from July 1 through July 31. The DAM program will be eliminated, and
replaced with the expanded SAM areas (effective April 7, 2008).
Changes to the SAM Program for Gillnet Gear
Under this final rule, in addition to the measures revised for
gillnet fisheries, the following requirements specific to the SAM and
DAM programs would apply. The SAM areas will be expanded, and all
gillnet fisheries operating within these areas during the restricted
time periods will be subject to the current SAM restrictions, plus the
following: A second buoy line will be allowed and the bottom one-third
of the buoy line may be composed of floating line. In addition, gillnet
fisheries would be allowed two configuration options for gillnet net
panel weak links as noted in the Other Northeast Gillnet Waters section
of this rule. The gillnet fisheries regulated under the SAM program
will be expanded to include Northeast anchored float gillnets. The
expanded SAM area will include the Great South Channel Restricted Area;
therefore, gillnet gear will be subject to the SAM program inside right
whale restricted areas during time periods when the requirements for
fishing inside these areas are no more conservative than the
surrounding waters (i.e., when the protections of right whale
restricted areas disappear). However, the more restrictive Great South
Channel Restricted Gillnet Area closure (April 1 through June 30) will
supercede the SAM program. As a result, gear modifications for fishing
with gillnet gear in the SAM area will apply in the Great South Channel
Restricted Gillnet Area from July 1 through July 31, and in the Great
South Channel Sliver Restricted Area from May 1 through July 31. The
DAM program will be eliminated, and replaced with the expanded SAM
areas (effective April 7, 2008).
Other Changes for All Trap/Pot and Gillnet Gear
DAM Program
The majority of the modifications in this final rule will become
effective on April 7, 2008, including the replacement of the DAM
program. Consequently, on April 7, 2008, when the SAM areas are
expanded, the expanded SAM program will replace the DAM program.
However, until April 7, 2008, the currently regulated trap/pot and
gillnet fisheries, will be subject to both the SAM and DAM programs.
After April 7, 2008, the currently regulated trap/pot and gillnet
fisheries, as well as those added to the ALWTRP, will be subject to the
expanded SAM program.
Groundlines
Under this final rule, for both trap/pot and gillnet fisheries, the
SAM program will be eliminated and replaced with broad-based gear
modifications, including a requirement that all groundlines must be
composed of sinking and/or neutrally buoyant line, effective on October
6, 2008 (unless otherwise required in the Cape Cod Bay Restricted Area
for trap/pot (January 1-May 15) or SAM areas).
Gear Marking
Under this final rule, NMFS will expand requirements to fisheries
and areas not previously regulated under the ALWTRP or required to mark
gear such as the following: Northeast drift gillnet; Northeast anchored
float gillnet; Northern Inshore State Trap/Pot Waters; LMA 6 portion of
Southern Nearshore Trap/Pot Waters; Mid/South Atlantic Gillnet Waters;
and Other Southeast Gillnet Waters (effective April 7, 2008). The gear
marking scheme will require one 4-inch (10.2 cm) colored mark midway
along the buoy line. Additionally, the gear marking scheme will require
all surface buoys to identify the vessel registration number, vessel
documentation number, Federal permit number, or whatever positive
identification marking is required by the vessel's home-port state
(effective April 7, 2008). Under this final rule, the color and marking
scheme for nets used in the Southeastern U.S. Atlantic shark gillnet
fishery will remain status quo and only buoy lines greater than 4 feet
(1.2 m) in length would need to be marked for this fishery.
Trap/Pot Gear Marking Colors
The ALWTRP will require fishermen to mark their trap/pot buoy lines
with one red 4-inch (10.2 cm) mark while they fish in the following
management areas: Cape Cod Bay Restricted Area, Northern Nearshore
Trap/Pot Waters, and Stellwagen Bank/Jeffreys Ledge. To remain
consistent with the gear marking color scheme in the North Atlantic,
under this final rule, NMFS will require red marking on the buoy lines
of trap/pot gear fished in Northern Inshore State Trap/Pot Waters. The
trap/pot gear marking color in the Great South Channel Restricted Area
is black. However, under this final rule, for consistency with nearby
management areas, the Great South Channel Restricted Area gear marking
color will be either black or red, depending on the area of overlap
with offshore (i.e., LMA 2/3 Overlap and LMA 3) and nearshore areas
(i.e., LMA 2 and the Outer Cape), respectively. The gear marking colors
for trap/pot gear in the Southern Nearshore Trap/Pot Waters and
Offshore Trap/Pot Waters will remain orange and black, respectively.
Gillnet Gear Marking Colors
Under this final rule, for consistency with the current gillnet
gear marking scheme in the Northeast Atlantic, NMFS will require one 4-
inch (10.2-cm) green mark midway along the buoy line for the two new
fisheries that will be added to the ALWTRP: Northeast drift gillnet and
Northeast anchored float gillnet.
Prior to this final rule, there were no gear marking requirements
for the two gillnet fisheries operating in the Mid/South Atlantic: the
Mid/South Atlantic anchored gillnet and Mid/South Atlantic drift
gillnet fisheries. Under this final rule, NMFS will require that these
fisheries mark their buoy lines with one 4-inch (10.2-cm) blue mark
midway along the buoy line.
Under this final rule, the Southeast Atlantic gillnet fishery will
be required to mark their buoy lines with one 4-inch (10.2-cm) yellow
mark midway on the buoy line in the same manner as the Mid/South
Atlantic gillnet fisheries. As mentioned above, the color and marking
scheme for nets used in the Southeastern U.S. Atlantic shark gillnet
fishery would remain status quo and only buoy lines greater than 4 feet
(1.2 m) in length will need to be marked.
[[Page 57111]]
Exempted Waters
Modifications to the exempted waters are effective on April 7,
2008.
Coastal Exempted Waters
To be consistent throughout the east coast, under this final rule,
with the exceptions detailed below, NMFS will exempt all marine and
tidal waters landward of the 72 COLREGS demarcation lines. The 72
COLREGS lines are well known and widely published lines of demarcation.
In four areas, Casco Bay (Maine), Portsmouth Harbor (New Hampshire),
the state of Massachusetts, and Long Island Sound and Gardiners Bay
(New York), NMFS will not use the 72 COLREGS lines and will instead
create different exemption lines. Any exemption lines for these areas,
as well as areas where the 72 COLREGS lines do not exist, are explained
in the Changes From the Proposed Rule sections (2) through (4) below.
Based on the public comments received and an analysis of the
available data, NMFS will use an exemption line for the coast of Maine
that is largely based on the line suggested by the Maine Department of
Marine Resources (Maine DMR). The final exemption line for Maine will
begin at the Maine-Canada border and extend south and west along the
Maine coastline to Odiornes Point, New Hampshire. The line will be
connected using a series of 25 buoys and islands along the Maine coast
(Figure 4). See the regulations in this final rule for the coordinates
of the Maine exemption line. See Changes From the Proposed Rule section
(2) below for further information on the rationale for the final Maine
exemption line.
Through this final rule, NMFS is modifying the exempted waters for
New Hampshire's three harbors, two as proposed and one slightly
modified. As proposed, NMFS will exempt Rye and Hampton Harbors
according to the lines drawn across the headlands which mark their
entrances to the sea. Portsmouth Harbor will not be exempted according
to the 72 COLREGS demarcation line (the only 72 COLREGS line found in
the state) because it will be exempted through the final exemption line
for Maine, as this line's final coordinate is located at Odiornes
Point, New Hampshire.
The exempted waters for Massachusetts will continue to include
state waters landward of the first bridge over any embayment, harbor,
or inlet. See the Changes From the Proposed Rule section (3) below for
further information on the rationale for the final Massachusetts
exemption line. This final rule will not modify the current exemption
lines for Massachusetts or Rhode Island, except for minor refinement of
the exemption line coordinates for Point Judith Pond and Quonochontaug
Pond Inlets in Rhode Island. However, under this final rule, NMFS will
clarify that the exemption line coordinates drawn for Narragansett Bay
and the Sakonnet River match the 72 COLREGS lines for these waters
(Figure 5).
In New York, with the exception of New York Harbor, all embayments,
harbors, and inlets are currently exempted under the ALWTRP. Under this
final rule, these exempted waters will remain unchanged with the
exception of the Long Island Sound and Gardiners Bay area. However,
NMFS will clarify that the exemption lines for Shinnecock Bay Inlet,
Moriches Bay Inlet, Fire Island Inlet, and Jones Inlet match the 72
COLREGS demarcation lines. In addition, NMFS will create an exemption
line for New York Harbor based on the 72 COLREGS line. This is a line
drawn from East Rockaway Inlet Breakwater Light to Sandy Hook Light.
Under this final rule, NMFS will exempt a portion of Block Island Sound
landward of the territorial sea baseline which extends from Watch Hill
Point, Rhode Island, to Montauk Point, New York (Figure 5). See the
Changes From the Proposed Rule section (4) below for further
information on the rationale for creating the Block Island Sound
exemption line.
NMFS clarifies that the entire shoreline of New Jersey would be
exempted landward of the 72 COLREGS demarcation lines. In doing this,
the exemption line for Barnegat Inlet will be relocated slightly east
of the current exemption line to make it consistent with the 72 COLREGS
demarcation line.
NMFS redefines the exemption line for Delaware Bay as the 72
COLREGS demarcation line. This is a line drawn from Cape May Light to
Harbor of Refuge Light; thence to the northernmost extremity of Cape
Henlopen (Figure 6). Along the Maryland and Virginia shorelines, two of
the four existing exemption lines match the 72 COLREGS lines. However,
the exemption line from Chincoteague to Ship Shoal Inlet crosses the 3-
nautical mile (5.6-km) state waters line, which is not consistent with
the 72 COLREGS lines. Under this final rule, NMFS clarifies that the
shoreline of Maryland and Virginia would be exempted landward of the 72
COLREGS lines. This includes using the 72 COLREGS line to exempt
Chesapeake Bay. This is a line drawn from Cape Charles Light to Cape
Henry Light (Figure 7). In addition, the existing exemption line for
Smith Island Inlet will be removed from the exempted waters section of
the regulations because the 72 COLREGS line for Chesapeake Bay includes
the entrance to this inlet.
The existing exemption lines in the Southeast (North Carolina to
Florida) will remain unchanged. However, Captain Sam's Inlet (South
Carolina) will be added to the exempted waters section of the
regulations because it does not have a 72 COLREGS line.
NMFS believes that the exemption lines contained in this final rule
are appropriate in light of the analysis of the most recent sightings
data from available sources, and will not create a substantial increase
in risk to large whales from fishing gear. NMFS will continue to work
in collaboration with state partners to monitor all exemption areas and
should new information become available regarding the exemption areas,
NMFS will share this information with the ALWTRT to determine if
changes to the exemption areas are warranted.
Offshore Exempted Areas
Based on a review of the best available scientific information,
NMFS has determined that exempting waters at depths greater than 275
fathoms (1,650 ft or 502.9 m) will not increase the risk of large whale
entanglement in groundlines, as most large whales are not known to dive
to these depths. To account for variations in groundline profiles, NMFS
added 5 fathoms (30 ft or 9.1 m) to achieve an offshore exemption depth
of 280 fathoms (1,680 ft or 512.1 m). Therefore, this final rule
exempts trap/pot and gillnet fishermen from the requirement to use
sinking and/or neutrally buoyant groundlines in waters deeper than 280
fathoms (1,680 ft or 512.1 m). Additionally, this final rule exempts
gillnet net panel weak link and anchoring requirements if the depth of
the float-line is in waters deeper than 280 fathoms (1,680 ft or 512.1
m).
Regulatory Language Changes
Changes listed below are effective on April 7, 2008 unless
otherwise noted.
Weak Links
The ALWTRT recommended that, for consistency, NMFS should change
all headings for weak links in the ALWTRP regulations from ``Weak Links
on all Buoy Lines,'' ``Buoy Weak Links,'' and ``Buoy Line Weak Links''
to simply ``Weak Links.'' Under the ALWTRP final rule, ``Buoy Line Weak
Links,'' or ``Net Panel Weak Links'' will be used for
[[Page 57112]]
clarification. NMFS also clarifies that weak links must be placed on
all floatation and/or weighted devices, etc. that are attached to the
buoy line, and not just the main buoy. This final rule adds to the
regulatory text that weak links must be designed such that the bitter
end (the loose end of the line that detaches from the weak link) of the
line is clean and free of any knots when the link breaks, and that
splices are not considered to be knots for the purposes of this
provision. The final rule clarifies that gillnets, traps/pots, anchors,
and leadline woven into the buoy line are not considered weighted
devices attached to the buoy line. Therefore, under this final rule,
when referring to the techniques for meeting the weak link
requirements, the wording will read, ``All buoys, flotation devices
and/or weights (except traps/pots [or gillnets], anchors, and leadline
woven into the buoy line), such as surface buoys, high flyers, sub-
surface buoys, toggles, window weights, etc. must be attached to the
buoy line with a weak link placed as close to each individual buoy,
flotation device and/or weight as operationally feasible and that meets
the following specifications''.
In a final rule published on January 10, 2002, the use of line \7/
16\ inch (1.11 cm) in diameter or less for all buoy lines was removed
as an option from the ALWTRP's Take Reduction Technology Lists, as the
breaking strength of \7/16\ inch (1.11 cm) line can vary dramatically
(67 FR 1300, January 10, 2002). Therefore, because the diameter of line
is not appropriate to use for risk reduction, NMFS will also change the
text that describes the list of approved weak links. Specifically, the
regulatory text referring to ``rope of appropriate diameter'' will be
changed to ``rope of appropriate breaking strength''.
Where the gear modification requirements are referred to, this
final rule includes reference to a brochure that describes techniques
for complying with these requirements and provide information about how
to obtain a copy.
This final rule amends the current regulatory text describing the
placement of weak links in the floatline of gillnet net panels.
Specifically, the text will be modified to change the requirements for
the placement of one weak link in gillnet net panels that are shorter
than 50 fathoms (300 ft or 91.4 m). This final rule modifies the
requirements in the Mid/South Atlantic Gillnet Waters (for anchored
gillnets) and adds requirements for the Other Southeast Gillnet Waters
as follows: ``Weak links must be placed in the center of the floatline
of each gillnet net panel up to and including 50 fathoms (300 ft or
91.4 m), or at least every 25 fathoms (150 ft or 45.7 m) along the
floatline for longer panels.'' This final rule also amends the
requirements for the placement of weak links in the SAM areas and other
applicable areas where more than one weak link is required for gillnet
net panels of lengths up to and including 50 fathoms, (300 ft or 91.4
m) as well as those greater than 50 fathoms (300 ft or 91.4 m).
Additionally, this final rule specifies two configuration options for
gillnet net panel weak links for anchored gillnet fisheries in the
Northeast (effective April 7, 2008, including SAM areas April 7, 2008,
and Mid/South Atlantic (that is not returned to port with the vessel),
as well as gillnet fisheries in the Southeast that are not returned to
port with the vessel (effective April 7, 2008). See the requirements
for anchored gillnets in the Other Northeast Gillnet Waters section of
this rule for the specifics on these configurations for gillnet net
panel weak links. The same configuration option would be required for
all gillnet net panels in a string.
Groundlines
This final rule clarifies that fishermen may use sinking and/or
neutrally buoyant line for their groundlines and buoy lines. Under this
final rule, from January 1 through May 15 fishermen will be allowed to
use sinking and/or neutrally buoyant groundlines in the Cape Cod Bay
Restricted Area. Similarly, for the SAM gear modifications, this final
rule will allow the use of sinking and/or neutrally buoyant
groundlines.
Where sinking and/or neutrally buoyant line is required for
groundlines, this final rule prohibits the attachment of flotation
devices, such as buoys and toggles. This clarifies the prohibition on
floating groundlines by expanding the prohibition to the attachment of
any devices that cause groundlines to float into the water column, to
reduce the risk of entangling large whales.
Other Regulatory Language Changes
The following changes to the current ALWTRP regulations are revised
to improve consistency and clarity (effective April 7, 2008).
Gillnet Take Reduction Technology List
In 2002, NMFS published a final rule (67 FR 1300, January 10, 2002)
that replaced the Gillnet Take Reduction