Fisheries of the Northeastern United States; Northeast Multispecies Fishery; Allowance of New Gear (Eliminator Trawl) in Specific Special Management Programs, 29098-29103 [E8-11303]
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Federal Register / Vol. 73, No. 98 / Tuesday, May 20, 2008 / Proposed Rules
months of the date of the receipt of the
petition on whether the petitioned
action is: (a) Not warranted, (b)
warranted, or (c) warranted but
precluded by other pending proposals.
Such 12-month findings are to be
published promptly in the Federal
Register.
On October 6, 2004, we received a
petition, dated October 6, 2004, from the
Center for Biological Diversity (CBD),
the Maricopa Audubon Society, and the
Arizona Audubon Council requesting
that the ‘‘Southwestern desert nesting
bald eagle population’’ be classified as
a DPS, that this DPS be reclassified from
a threatened species to an endangered
species, and that we concurrently
designate critical habitat for the DPS
under the Act.
On March 27, 2006, the CBD and the
Maricopa Audubon Society filed a
lawsuit against the U.S. Department of
the Interior and the Service for failing to
make a timely finding on the petition.
The parties reached a settlement, and
the Service agreed to complete its
petition finding by August 2006. On
August 30, 2006 (71 FR 51549), we
announced our 90-day finding that the
petition did not present substantial
scientific or commercial information
indicating that the petitioned action
may be warranted.
On January 5, 2007, the CBD and the
Maricopa Audubon Society filed a
lawsuit challenging the Service’s 90-day
finding that the ‘‘Sonoran Desert
population’’ of the bald eagle did not
qualify as a DPS, and further
challenging the Service’s 90-day finding
that the population should not be uplisted to endangered status.
On July 9, 2007 (72 FR 37346), we
published the final delisting rule for
bald eagles in the lower 48 States. In
that final delisting rule, we stated that
our findings on the status of the
Sonoran Desert population of bald
eagles superseded our 90-day petition
finding because the final delisting rule
constituted a final decision on whether
the Sonoran Desert population of bald
eagles qualified for listing as a DPS
under the Act.
On March 5, 2008, the U.S. District
Court for the District of Arizona ruled in
favor of the CBD and the Maricopa
Audubon Society. The court order
(Center for Biological Diversity v.
Kempthorne, CV 07–0038–PHX–MHM
(D. Ariz)) was filed on March 6, 2008.
The court ruled for the plaintiffs and
ordered the Service to:
(1) Conduct a status review of the
Sonoran Desert area bald eagle
population pursuant to the Act to
determine whether listing that
population as a DPS is warranted, and
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17:03 May 19, 2008
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if so, whether listing that DPS as
threatened or endangered pursuant to
the Act is warranted;
(2) Issue a 12-month finding on
whether listing the Sonoran Desert area
bald eagle population as a DPS is
warranted, and if so, whether listing
that DPS as threatened or endangered is
warranted; and
(3) Issue the 12-month finding within
9 months of the court order pursuant to
16 U.S.C. 1533(b)(3)(B), which translates
to on or before December 5, 2008.
Further, the court enjoined the
Service’s application of the July 9, 2007
(72 FR 37346), final delisting rule to the
Sonoran Desert population of bald
eagles pending the outcome of our
status review and 12-month petition
finding. The court order was effective as
of March 6, 2008, the date it was filed.
On May 1, 2008, we published a final
rule (73 FR 23966) listing the potential
Sonoran Desert area bald eagle DPS as
threatened under the Act in response to
the court order. Please refer to the map
and final rule published on May 1, 2008
(73 FR 23966) for details of the
geographic area affected by this action.
At this time, we are soliciting new
information on the status of and
potential threats to the Sonoran Desert
population of bald eagles. We will base
our new determination as to whether
listing is warranted on a review of the
best scientific and commercial
information available, including all
such information received as a result of
this notice. For more information on the
biology, habitat, and range of the
Sonoran Desert population of bald
eagles, please refer to our previous 90day finding published in the Federal
Register on August 30, 2006 (71 FR
51549), and our final delisting rule for
the bald eagle published in the Federal
Register on July 9, 2007 (72 FR 37346).
Author
The primary author of this notice is
the staff of the Arizona Ecological
Services Office.
Authority
The authority for this action is the
Endangered Species Act of 1973 (16
U.S.C. 1531 et seq.).
Dated: May 8, 2008.
Kenneth Stansell,
Acting Director, U.S. Fish and Wildlife
Service.
[FR Doc. E8–11052 Filed 5–19–08; 8:45 am]
BILLING CODE 4310–55–P
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 080306389–8391–01]
RIN 0648–AW53
Fisheries of the Northeastern United
States; Northeast Multispecies
Fishery; Allowance of New Gear
(Eliminator Trawl) in Specific Special
Management Programs
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule; request for
comments.
AGENCY:
SUMMARY: NMFS proposes approval for
using another type of trawl gear known
as the ‘‘eliminator trawl’’ in the Regular
B Days-at-Sea (DAS) Program and the
Eastern U.S./Canada Haddock Special
Access Program (SAP). Vessels fishing
in the Regular B DAS Program and the
Eastern U.S./Canada Haddock SAP must
use approved trawl gear in order to
reduce the catch of multispecies
(groundfish) stocks of concern. The
Northeast (NE) Regional Administrator,
NMFS, may approve additional gears for
use in these programs if research
demonstrates that the gear meets
specific standards for the reduction of
catch of stocks of concern. The intent of
this action is to reduce catch of stocks
of concern in the NE multispecies
fishery.
DATES: Comments must be received by
June 4, 2008.
ADDRESSES: You may submit comments,
identified by 0648–AW53, by any one of
the following methods:
• Electronic Submissions: Submit all
electronic public comments via the
Federal e-rulemaking portal: https://
www.regulations.gov.
• Mail: Paper, disk, or CD-ROM
comments should be sent to Patricia A.
Kurkul, Regional Administrator,
National Marine Fisheries Service, One
Blackburn Drive, Gloucester, MA 01930.
Mark the outside of the envelope,
‘‘Comments on the eliminator trawl.’’
• Fax: (978) 281–9135.
Instructions: All comments received
are part of the public record and will
generally be posted to https://
www.regulations.gov without change.
All Personal Identifying Information (for
example, name, address, etc.)
voluntarily submitted by the commenter
may be publically accessible. Do not
submit Confidential Business
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Information or otherwise sensitive or
protected information.
NMFS will accept anonymous
comments. Attachments to electronic
comments will be accepted in Microsoft
Word, Excel, WordPerfect, or Adobe
PDF formats only.
Copies of the Technical Report
‘‘Bycatch Reduction in the Directed
Haddock Bottom Trawl Fishery’’ and a
diagram of the eliminator trawl may be
obtained from NMFS at the mailing
address specified above; telephone (978)
281–9315. NMFS prepared an Initial
Regulatory Flexiblity Analysis (IRFA),
which is contained in the Classification
section of this proposed rule.
FOR FURTHER INFORMATION CONTACT:
Thomas Warren, Fishery Policy Analyst,
(978) 281–9347, fax (978) 281–9135.
SUPPLEMENTARY INFORMATION: The NE
Multispecies Fishery Management Plan
(FMP) contains broadly applied input
control regulations that are designed to
protect stocks that need reductions in
fishing mortality. Because such
regulations apply in a broad manner,
they not only restrict fishing effort on
stocks of concern, but also restrict
fishing effort on stocks that do not need
reductions in fishing mortality.
Therefore, SAPs were implemented in
the FMP to increase access to stocks that
do not need reductions in fishing
mortality. A SAP authorizes additional
fishing effort in order to allow an
increased yield in specific stocks
without undermining the achievement
of the goals of the FMP. For example,
SAPs may allow the use of Category B
DAS or allow temporary access to a
closed area to increase access to
particular stocks. To help ensure that
catch of stocks of concern is reduced to
acceptable levels, vessels fishing in a
SAP are subject to additional fishing
restrictions than those that apply to
vessels fishing in the NE multispecies
fishery at large. Framework Adjustment
(FW) 40–A (69 FR 67780; November 19,
2004) implemented the Regular B DAS
Program and the Eastern U.S./Canada
Haddock special management programs
that currently include gear restrictions
designed to substantially reduce the
catch of stocks of concern.
The Regular B DAS Program, which
initially did not contain any gear
restrictions, was later modified under
FW 42 (71 FR 62156; October 23, 2006)
to require trawl vessels to use a haddock
separator trawl in order to further
reduce the potential for vessels to catch
stocks of concern-- notably, cod,
yellowtail flounder, and winter
flounder. The Eastern U.S./Canada
Haddock SAP, from its inception,
contained a more restrictive
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requirement specifying that any vessel
fishing in the program must use a
haddock separator trawl. FW 42 also
authorized the Regional Administrator
to approve other gear types for use in
the Regular B DAS Program and the
Eastern U.S./Canada Haddock SAP to
reduce catch of stocks of concern, based
upon approved gear standards, but did
not contain any standards for evaluating
proposed additional gear types. On
December 26, 2007, based upon
recommendations of the New England
Fishery Management Council (Council),
NMFS implemented specific gear
standards that could be used to evaluate
additional gear proposed for use in
these programs to reduce catch of stocks
of concern and clarified the process by
which new gear would be considered
(72 FR 72965).
The December 26, 2007 rule specified
that, to be approved, new gear must first
be compared to an appropriately
selected control gear. Based on this
comparison, new gear can be approved
if it meets one of the following two
standards: (1) Use of the gear must
result in a statistically significant
reduction, compared to the control gear,
of at least 50 percent (by weight, on a
trip-by-trip basis) in catch of each
regulated species stock of concern, or
other non-groundfish stocks that are
overfished or subject to overfishing
identified by the Council; or (2) the use
of the gear must result in a catch of each
regulated NE multispecies stock of
concern, or other non-groundfish stocks
that are overfished or subject to
overfishing identified by the Council,
that is less than 5 percent of the total
catch of regulated groundfish (by
weight, on a trip-by-trip basis). Neither
of these requirements apply to regulated
species identified by the Council as not
being subject to gear performance
standards. Because many species in the
fishery are caught together, and the
dynamic nature of the status of stocks,
the performance standard must have a
reasonable amount of flexibility in order
to be practical.
One of these standards must be met in
a completed experiment, where
comparisons of new gear are made to an
appropriately selected control gear that
has been reviewed according to the
standards established by the Council’s
research policy, before the gear can be
considered and approved by the
Regional Administrator. In addition, a
request for approval of the use of
additional gear in the Regular B DAS
Program and the Eastern U.S./Canada
Haddock SAP must be made by either
the Council or the Council’s Executive
Committee.
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Regarding the proposal to approve the
gear specified in this action, an
experiment was conducted by the
University of Rhode Island, Rhode
Island Sea Grant Program, in
conjunction with members of the fishing
industry, from September 2004 through
July 2006, to investigate a large-mesh
experimental net known as the
‘‘eliminator trawl’’, designed to capture
haddock while reducing the catch of
cod and other species. Two fishing
vessels with equivalent length,
horsepower, and fishing capacity
participated in the study, and compared
the eliminator trawl with a control net
(constructed with currently legal
specifications) using side-by-side tows.
Four trips, conducted in the months of
June, November, December, and April,
resulted in 107 comparison tows, 100 of
which were analyzed. The final report,
‘‘Bycatch Reduction in the Directed
Haddock Bottom Trawl Fishery’’ (URI
Fisheries Center Technical Report: 01–
06; October 2006) included the
following results and conclusions:
Haddock was the dominant species
caught in the experimental net, and
represented 77 percent of the total
catch. The overall rounded ratio of
haddock to cod in the experimental and
control nets was 20:1 and 3:1,
respectively. A statistical comparison by
tow indicated that there was a
significant difference in the catch
weights between the control and the
experimental nets for cod, yellowtail
flounder, winter flounder, witch
flounder, American plaice, white hake,
monkfish, skates, and other nongroundfish species. The eliminator trawl
caught less of these species than the
control net, whereas there was no
statistical difference in the weight of
haddock caught between the two nets.
A February 5, 2007, review by the
Northeast Fisheries Science Center,
NMFS’s NE State, Federal, and
Constituent Programs Office noted the
successful conclusion of the research
project, and the Council’s Research
Steering Committee reviewed the
research on March 29, 2007. Both
reviews agreed that the experiment
successfully demonstrated that the net
design allowed the harvest of haddock,
while reducing catches of cod and other
stocks of concern. Although the NE
Multispecies Plan Development Team
did not review the experimental results,
a February 8, 2008, memorandum from
the Council’s Executive Director to the
Council indicated that the Council staff
had reviewed the experimental data and
concluded that the eliminator trawl
clearly met the first regulatory standard
for approval of new gear requiring a
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showing of more than a 50- percent
reduction compared to the control gear
of catch of regulated species stocks of
concern. On February 13, 2008, the
Council passed a motion that the
haddock eliminator trawl be
recommended to the Regional
Administrator for use in the Eastern
U.S./Canada Haddock SAP and the
Regular B DAS Program, and on
February 19, 2008, the Council sent the
Regional Administrator a letter
requesting approval of this gear.
Based upon the final report, ‘‘Bycatch
Reduction in the Directed Haddock
Bottom Trawl Fishery,’’ and the
Council’s February 19, 2008, letter,
NMFS is proposing approval of the
eliminator trawl. The pertinent
information indicates that the catch of
each regulated species stock of concern,
as well as other species, declined by
more than 50 percent with use of the
eliminator trawl, which complies with
the first standard for approval of
additional gear. The proposed
eliminator trawl net specifications are
based upon input from the individuals
involved in the eliminator trawl
research, and NMFS gear experts.
Approval of the eliminator trawl would
allow trawl vessels fishing in the
Regular B DAS Program or the Eastern
U.S./Canada Haddock SAP a choice of
whether to use the haddock separator
trawl or the eliminator trawl. The size
of the eliminator trawl specified would
be appropriate for fishing vessels with
engines of at least 600 horsepower. The
results of the experiment cannot be used
to extrapolate to smaller scale
eliminator trawl gear that could be
readily used by smaller horsepower
vessels.
The Council identified that the gear
performance standards do not apply to
haddock, pollock, and redfish. Haddock,
pollock, and redfish are target stocks for
which no reductions in fishing mortality
are required. The researchers could not
conduct statistical tests on Atlantic
halibut because the species was not
present in sufficient numbers (defined
by the researchers as present in at least
10 paired tows), and therefore the gear
standard could not be applied in a
meaningful way to Atlantic halibut.
Because Atlantic halibut is caught in
very low numbers by the trawl fishery,
and is subject to a possession limit of
one fish per trip, NMFS has determined
that the lack of information on the
compliance of Atlantic halibut with gear
standards is not sufficient justification
for disapproval of the eliminator trawl.
Furthermore, it is likely that the
selectivity of the eliminator trawl for
Atlantic halibut is low, given the
similarity in body shape and ecology of
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the Atlantic halibut to the other
flatfishes, which were less numerous in
the eliminator trawl. This application of
the gear standard is consistent with the
intent of the Council (i.e., reasonable
flexibility in application of the gear
standards) and the goal of providing
opportunities and incentives for the
fishing industry to utilize gear that
results in substantial reductions in
bycatch.
NMFS is not proposing that vessels
must have their eliminator trawl net
inspected and certified by a net
manufacturer, as suggested by Council
staff in the attachment to the Council’s
February 19, 2008, letter to NMFS. The
stated concern is that slight
modifications in the net configuration
could alter the effectiveness of the net
in reducing catches of species of
concern. Inspection by a net
manufacturer would not prevent a
vessel operator from modifying his/her
net after such an inspection occurred,
would impose additional costs to the
industry, would be difficult to enforce,
and would be redundant, because the
net manufacturer can verify to the net
purchaser what he/she is purchasing at
the time of purchase. The fisherman is
responsible for the compliance of his/
her gear with the regulations, and NMFS
and the United States Coast Guard
enforce the gear regulations.
Furthermore, this requirement was not
proposed by the Council (based on the
Council’s pertinent motion).
Classification
NMFS has determined that the
proposed rule is consistent with the
FMP and has preliminarily determined
that this rule is consistent with the
Magnuson-Stevens Fishery
Conservation and Management Act and
other applicable laws.
An initial regulatory flexibility
analysis (IRFA) has been prepared, as
required by section 603 of the
Regulatory Flexibility Act (RFA),
consisting of this proposed rule, the
following analysis, and the Categorical
Exclusion prepared for this action. The
IRFA below describes the economic
impact this proposed rule, if adopted,
would have on small entities.
Allowing the use of the eliminator
trawl in the Regular B DAS Program and
the Eastern U.S./Canada Haddock SAP
would provide the fishing industry
more flexibility in the use of trawl gear
that minimizes catch of stocks of
concern by providing them with a
choice of whether to use the haddock
separator trawl or the eliminator trawl.
Vessels fishing under a Regular B DAS
in these programs must comply with
restrictive landing limits of various
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species. The choice of two nets would
enable a vessel owner to decide which
net is the most cost effective means of
targeting haddock and complying with
the landing restrictions. A description of
the objectives and legal basis for the
proposed eliminator trawl is contained
in the SUMMARY of this proposed rule.
Under the Small Business
Administration (SBA) size standards for
small fishing entities ($ 4.0 million in
annual gross sales), all permitted and
participating vessels in the groundfish
fishery are considered to be small
entities and, therefore, there are no
disproportionate impacts between large
and small entities. Gross sales by any
one entity (vessel) do not exceed this
threshold. The maximum number of
small entities that could be affected by
the proposed approval of the eliminator
trawl are approximately 1,200 vessels;
i.e., those issued limited access NE
multispecies DAS permits that have an
allocation of Category A or B DAS.
Realistically, however, the number of
vessels that choose to fish in either of
these programs, and that would
therefore be subject to the associated
restrictions, including the use of either
the haddock separator trawl or the
eliminator trawl, would be substantially
smaller. For example, in fishing year
(FY) 2005, 132 vessels fished in either
the Regular B DAS Program or the
Eastern U.S./Canada Haddock SAP. In
FY 2006, there were only 45 vessels that
fished in either program. Although it is
possible that, under future
circumstances, more vessels may elect
to participate in these programs, a large
increase in the numbers of participants
is unlikely. Furthermore, some
participants in the Regular B DAS
Program and in the SAP may not have
sufficient engine horsepower to use the
eliminator trawl, and, therefore, may not
be able to use the trawl.
Based on information from a
commercial net manufacturer, the cost
of purchasing a new eliminator trawl
net is approximately $ 13,000. A squid
trawl net could be modified into an
eliminator trawl for approximately $
1,000, by replacing the last belly portion
of the net and putting in a rockhopper
sweep. If 130 vessels fished in either of
the special management programs that
require the use of a specialized trawl,
and the vessel operators decided to
purchase the eliminator trawl net, the
total cost to the industry would be
approximately $1,690,000. It is likely
that many vessels that have fished in
these programs in the past using a
separator trawl may choose not to
purchase an eliminator trawl. Vessels
choosing to use the eliminator trawl
would incur the purchase cost and other
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adjustment costs. The decision to do so,
and to thereby fish in a special
management program offering
additional revenue opportunities is a
voluntary decision based on the
individual vessel’s assessment of
profitability.
Because of the context in which this
action is proposed, there are only two
alternatives under consideration: The no
action alternative and approval of the
eliminator trawl. Consideration of
another trawl gear (i.e., a third
alternative) in addition to the eliminator
trawl is not proposed at this time. The
process of conducting gear research and
reviewing such research is time
consuming and costly, and the
standards for approval must be met.
Although other trawl gear research is
either underway or proposed, the
eliminator trawl is the only gear that has
been vetted through the review process
and recommended by the Council.
Additional research is being proposed
by two of the co-authors of ‘‘Bycatch
Reduction in the Directed Haddock
Bottom Trawl Fishery’’ that will
investigate the use of an eliminator
trawl net designed for smaller vessels
with 250 to 550 horsepower engines.
Performance standards rather than
design standards are utilized for the
evaluation of new trawl gear, in order to
provide conservation engineers
flexibility in design and a meaningful
standard for the achievement of the goal
of bycatch reduction. The performance
standards under § 648.85(b)(6)(iv)(J)(2)
were developed for the specific purpose
of evaluating additional fishing gear for
these special management programs.
The proposed action would not
modify any collection of information,
reporting, or recordkeeping
requirements. The proposed net does
not duplicate, overlap, or conflict with
any other Federal rules.
Dated: May 14, 2008.
John Oliver,
Deputy Assistant Administrator for
Operations, National Marine Fisheries
Service.
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PART 648—FISHERIES OF THE
NORTHEASTERN UNITED STATES
1. The authority citation for part 648
continues to read as follows:
Authority: 16 U.S.C. 1801 et seq.
2. In § 648.2, new definitions for
‘‘fishing circle,’’ ‘‘stretched mesh,’’ and
‘‘sweep’’ are added in alphabetical
order, to read as follows:
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Definitions.
*
*
*
*
*
Fishing circle, with respect to the NE
multispecies limited access fishery,
means the calculated circumference of a
bottom trawl based on the number of
meshes and stretched mesh length at the
narrow, aft end of the square of the net.
*
*
*
*
*
Stretched mesh, with respect to the
NE multispecies eliminator trawl, means
mesh that is pulled so that slack in the
mesh is eliminated and the mesh
opening is closed.
*
*
*
*
*
Sweep, with respect to the NE
multispecies limited access fishery,
means the part of a bottom trawl that,
during normal use, is in contact with
the sea floor along the outer edges of the
lower webbing of the net.
*
*
*
*
*
3. In § 648.14, paragraphs (a)(132) and
(b)(81) are revised to read as follows:
§ 648.14
Prohibitions.
(a) * * *
(132) If fishing with trawl gear under
a NE multispecies DAS in the Eastern
U.S./Canada defined in
§ 648.85(a)(1)(ii), fail to fish with a
haddock separator trawl or a flounder
trawl net, as specified in
§ 648.85(a)(3)(iii), unless otherwise
allowed under the Eastern U.S./Canada
Haddock SAP rules in
§ 648.85(b)(8)(v)(E).
*
*
*
*
*
(b) * * *
(81) If fishing in the Regular B DAS
Program specified in § 648.85(b)(6), fail
to use a haddock separator trawl as
described under § 648.85(a)(3)(iii)(A), or
other approved gear as described under
§ 648.85(b)(6)(iv)(J).
*
*
*
*
*
4. In § 648.85, paragraphs
(b)(6)(iv)(J)(1) and (b)(8)(v)(E)
introductory heading and (b)(8)(v)(E)(1)
are revised, and paragraph (b)(6)(iv)(J)(3)
is added to read as follows:
§ 648.85
For the reasons stated in the
preamble, 50 CFR part 648 is proposed
to be amended as follows:
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§ 648.2
Special management programs.
*
*
*
*
*
(b) * * *
(6) * * *
(iv) * * *
(J) * * *
(1) Vessels fishing with trawl gear in
the Regular B DAS Program must use
the haddock separator trawl or
eliminator trawl net, as described under
paragraphs (a)(3)(iii)(A) and
(b)(6)(iv)(J)(3) of this section,
respectively, or other type of gear if
approved as described under this
paragraph (b)(6)(iv)(J). Other gear may
be on board the vessel, provided it is
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29101
stowed when the vessel is fishing under
the Regular B DAS Program.
*
*
*
*
*
(3) Eliminator Trawl. The eliminator
trawl is a four-seam bottom groundfish
trawl designed to reduce the bycatch of
cod while retaining or increasing the
catch of haddock, when compared to
traditional groundfish trawls. An
eliminator trawl must be constructed in
accordance with the following
standards:
(i) The net must be constructed with
four seams (i.e., a net with a top and
bottom panel and two side panels), and
include at least the following net
sections as depicted in Figure 1 of this
part ‘‘Nomenclature for 4–seam
eliminator trawl’’ (this figure is also
available from the Administrator,
Northeast Region): Top jib, bottom jib,
jib side panels (x 2), top wing, bottom
wing, wing side panels (x 2), square,
bunt, square side panels (x 2), first top
belly, first bottom belly, first belly side
panels (x 2), second top belly, second
bottom belly, second belly side panels
(x 2), and third bottom belly.
(ii) The first bottom belly, bunt, the
top and bottom wings, and the top and
bottom jibs, jib side panels, and wing
side panels (the first bottom belly and
all portions of the net in front of the first
bottom belly, with the exception of the
square and the square side panels) must
be at least two meshes long in the fore
and aft direction. For these net sections
the stretched length of any single mesh
must be at least 7.9 ft (240 cm).
(iii) Mesh size in all other sections
must be consistent with mesh size
requirements specified under § 648.80
and meet the following minimum
specifications: Each mesh in the square,
square side panels, and second bottom
belly must be 31.5 inches (80 cm); each
mesh in the first and second top belly,
the first belly side panels, and the third
bottom belly must be at least 7.9 inches
(20 cm); and 6 inches or larger in
sections following the second top belly
and third bottom belly sections, all the
way to the codend. The mesh size
requirements of the top sections apply
to the side panel sections.
(iv) The trawl must have a fishing
circle of at least 398 ft (121.4 m). This
number is calculated by separately
counting the number of meshes for each
section of the net at the wide, fore end
of the first bottom belly, and then
calculating a stretched length as follows:
For each section of the net (first bottom
belly, two belly side panels and first top
belly) multiply the number of meshes
times the length of each stretched mesh
to get the stretched mesh length for that
section, and then add the sections
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together. For example, if the wide, fore
end of the bottom belly of the eliminator
trawl is 22 meshes (and the mesh is at
least 7.9 ft (240 cm)), the stretched mesh
length for that section of the net is
derived by multiplying 22 times 7.9 ft
(240 cm) and equals 173.2 ft (52.8 m).
The top and sides (x 2) of the net at this
point in the trawl are 343 meshes (221
+ 61 + 61, respectively) (each 7.9 inches
(20 cm)), which equals 225.1 ft (68.6 m)
stretched length. The stretched lengths
for the different sections of mesh are
added together (173.2 ft + 225.1 ft (52.8
+ 68.6 m)) and result in the length of the
fishing circle, in this case 398.3 ft (121.4
m).
(v) The trawl must have at least three
1–square meter or larger kite panels on
the forward end of the square to help
maximize headrope height, for the
purpose of capturing rising fish. A kite
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17:03 May 19, 2008
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panel is a flat structure, usually semiflexible used to modify the shape of
trawl and mesh openings by providing
lift when a trawl is moving through the
water.
(vi) The sweep must consist of
rockhoppers, which are graduated from
16–inch (40–cm) diameter in the center
down to 12–inch (30–cm) diameter at
the wing ends. There must be six or
fewer 12 to16–inch (30 to 40–cm)
rockhopper discs over any 10–ft (3.0 m)
length of the sweep. The 12 to16 inch
(30 to 40–cm) discs must be spaced
evenly, with one disc placed
approximately every 2 ft (60 cm) along
the sweep. The 12 to 16–inch (30 to 40–
cm) discs must be separated by smaller
discs, no larger than 3.5 inches (8.8 cm)
in diameter.
*
*
*
*
*
(8) * * *
PO 00000
Frm 00018
Fmt 4702
Sfmt 4702
(v) * * *
(E) Gear requirement (1) A NE
multispecies vessel fishing in the
Eastern U.S./Canada Haddock SAP must
use the haddock separator trawl or
eliminator trawl net, as described under
paragraphs (a)(3)(iii)(A) and
(b)(6)(iv)(J)(3) of this section,
respectively, or other type of gear, if
approved as described under this
paragraph (b)(8)(v)(E). No other type of
fishing gear may be on the vessel when
on a trip in the Eastern U.S./Canada
Haddock SAP, with the exception of a
flounder net, as described in paragraph
(a)(3)(iii) of this section, provided that
the flounder net is stowed in accordance
with § 648.23(b).
*
*
*
*
*
5. In part 648, add Figure 1 as follows:
BILLING CODE 3510–22–S
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Federal Register / Vol. 73, No. 98 / Tuesday, May 20, 2008 / Proposed Rules
Agencies
[Federal Register Volume 73, Number 98 (Tuesday, May 20, 2008)]
[Proposed Rules]
[Pages 29098-29103]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-11303]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 648
[Docket No. 080306389-8391-01]
RIN 0648-AW53
Fisheries of the Northeastern United States; Northeast
Multispecies Fishery; Allowance of New Gear (Eliminator Trawl) in
Specific Special Management Programs
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Proposed rule; request for comments.
-----------------------------------------------------------------------
SUMMARY: NMFS proposes approval for using another type of trawl gear
known as the ``eliminator trawl'' in the Regular B Days-at-Sea (DAS)
Program and the Eastern U.S./Canada Haddock Special Access Program
(SAP). Vessels fishing in the Regular B DAS Program and the Eastern
U.S./Canada Haddock SAP must use approved trawl gear in order to reduce
the catch of multispecies (groundfish) stocks of concern. The Northeast
(NE) Regional Administrator, NMFS, may approve additional gears for use
in these programs if research demonstrates that the gear meets specific
standards for the reduction of catch of stocks of concern. The intent
of this action is to reduce catch of stocks of concern in the NE
multispecies fishery.
DATES: Comments must be received by June 4, 2008.
ADDRESSES: You may submit comments, identified by 0648-AW53, by any one
of the following methods:
Electronic Submissions: Submit all electronic public
comments via the Federal e-rulemaking portal: https://
www.regulations.gov.
Mail: Paper, disk, or CD-ROM comments should be sent to
Patricia A. Kurkul, Regional Administrator, National Marine Fisheries
Service, One Blackburn Drive, Gloucester, MA 01930. Mark the outside of
the envelope, ``Comments on the eliminator trawl.''
Fax: (978) 281-9135.
Instructions: All comments received are part of the public record
and will generally be posted to https://www.regulations.gov without
change. All Personal Identifying Information (for example, name,
address, etc.) voluntarily submitted by the commenter may be publically
accessible. Do not submit Confidential Business
[[Page 29099]]
Information or otherwise sensitive or protected information.
NMFS will accept anonymous comments. Attachments to electronic
comments will be accepted in Microsoft Word, Excel, WordPerfect, or
Adobe PDF formats only.
Copies of the Technical Report ``Bycatch Reduction in the Directed
Haddock Bottom Trawl Fishery'' and a diagram of the eliminator trawl
may be obtained from NMFS at the mailing address specified above;
telephone (978) 281-9315. NMFS prepared an Initial Regulatory
Flexiblity Analysis (IRFA), which is contained in the Classification
section of this proposed rule.
FOR FURTHER INFORMATION CONTACT: Thomas Warren, Fishery Policy Analyst,
(978) 281-9347, fax (978) 281-9135.
SUPPLEMENTARY INFORMATION: The NE Multispecies Fishery Management Plan
(FMP) contains broadly applied input control regulations that are
designed to protect stocks that need reductions in fishing mortality.
Because such regulations apply in a broad manner, they not only
restrict fishing effort on stocks of concern, but also restrict fishing
effort on stocks that do not need reductions in fishing mortality.
Therefore, SAPs were implemented in the FMP to increase access to
stocks that do not need reductions in fishing mortality. A SAP
authorizes additional fishing effort in order to allow an increased
yield in specific stocks without undermining the achievement of the
goals of the FMP. For example, SAPs may allow the use of Category B DAS
or allow temporary access to a closed area to increase access to
particular stocks. To help ensure that catch of stocks of concern is
reduced to acceptable levels, vessels fishing in a SAP are subject to
additional fishing restrictions than those that apply to vessels
fishing in the NE multispecies fishery at large. Framework Adjustment
(FW) 40-A (69 FR 67780; November 19, 2004) implemented the Regular B
DAS Program and the Eastern U.S./Canada Haddock special management
programs that currently include gear restrictions designed to
substantially reduce the catch of stocks of concern.
The Regular B DAS Program, which initially did not contain any gear
restrictions, was later modified under FW 42 (71 FR 62156; October 23,
2006) to require trawl vessels to use a haddock separator trawl in
order to further reduce the potential for vessels to catch stocks of
concern-- notably, cod, yellowtail flounder, and winter flounder. The
Eastern U.S./Canada Haddock SAP, from its inception, contained a more
restrictive requirement specifying that any vessel fishing in the
program must use a haddock separator trawl. FW 42 also authorized the
Regional Administrator to approve other gear types for use in the
Regular B DAS Program and the Eastern U.S./Canada Haddock SAP to reduce
catch of stocks of concern, based upon approved gear standards, but did
not contain any standards for evaluating proposed additional gear
types. On December 26, 2007, based upon recommendations of the New
England Fishery Management Council (Council), NMFS implemented specific
gear standards that could be used to evaluate additional gear proposed
for use in these programs to reduce catch of stocks of concern and
clarified the process by which new gear would be considered (72 FR
72965).
The December 26, 2007 rule specified that, to be approved, new gear
must first be compared to an appropriately selected control gear. Based
on this comparison, new gear can be approved if it meets one of the
following two standards: (1) Use of the gear must result in a
statistically significant reduction, compared to the control gear, of
at least 50 percent (by weight, on a trip-by-trip basis) in catch of
each regulated species stock of concern, or other non-groundfish stocks
that are overfished or subject to overfishing identified by the
Council; or (2) the use of the gear must result in a catch of each
regulated NE multispecies stock of concern, or other non-groundfish
stocks that are overfished or subject to overfishing identified by the
Council, that is less than 5 percent of the total catch of regulated
groundfish (by weight, on a trip-by-trip basis). Neither of these
requirements apply to regulated species identified by the Council as
not being subject to gear performance standards. Because many species
in the fishery are caught together, and the dynamic nature of the
status of stocks, the performance standard must have a reasonable
amount of flexibility in order to be practical.
One of these standards must be met in a completed experiment, where
comparisons of new gear are made to an appropriately selected control
gear that has been reviewed according to the standards established by
the Council's research policy, before the gear can be considered and
approved by the Regional Administrator. In addition, a request for
approval of the use of additional gear in the Regular B DAS Program and
the Eastern U.S./Canada Haddock SAP must be made by either the Council
or the Council's Executive Committee.
Regarding the proposal to approve the gear specified in this
action, an experiment was conducted by the University of Rhode Island,
Rhode Island Sea Grant Program, in conjunction with members of the
fishing industry, from September 2004 through July 2006, to investigate
a large-mesh experimental net known as the ``eliminator trawl'',
designed to capture haddock while reducing the catch of cod and other
species. Two fishing vessels with equivalent length, horsepower, and
fishing capacity participated in the study, and compared the eliminator
trawl with a control net (constructed with currently legal
specifications) using side-by-side tows. Four trips, conducted in the
months of June, November, December, and April, resulted in 107
comparison tows, 100 of which were analyzed. The final report,
``Bycatch Reduction in the Directed Haddock Bottom Trawl Fishery'' (URI
Fisheries Center Technical Report: 01-06; October 2006) included the
following results and conclusions: Haddock was the dominant species
caught in the experimental net, and represented 77 percent of the total
catch. The overall rounded ratio of haddock to cod in the experimental
and control nets was 20:1 and 3:1, respectively. A statistical
comparison by tow indicated that there was a significant difference in
the catch weights between the control and the experimental nets for
cod, yellowtail flounder, winter flounder, witch flounder, American
plaice, white hake, monkfish, skates, and other non- groundfish
species. The eliminator trawl caught less of these species than the
control net, whereas there was no statistical difference in the weight
of haddock caught between the two nets.
A February 5, 2007, review by the Northeast Fisheries Science
Center, NMFS's NE State, Federal, and Constituent Programs Office noted
the successful conclusion of the research project, and the Council's
Research Steering Committee reviewed the research on March 29, 2007.
Both reviews agreed that the experiment successfully demonstrated that
the net design allowed the harvest of haddock, while reducing catches
of cod and other stocks of concern. Although the NE Multispecies Plan
Development Team did not review the experimental results, a February 8,
2008, memorandum from the Council's Executive Director to the Council
indicated that the Council staff had reviewed the experimental data and
concluded that the eliminator trawl clearly met the first regulatory
standard for approval of new gear requiring a
[[Page 29100]]
showing of more than a 50- percent reduction compared to the control
gear of catch of regulated species stocks of concern. On February 13,
2008, the Council passed a motion that the haddock eliminator trawl be
recommended to the Regional Administrator for use in the Eastern U.S./
Canada Haddock SAP and the Regular B DAS Program, and on February 19,
2008, the Council sent the Regional Administrator a letter requesting
approval of this gear.
Based upon the final report, ``Bycatch Reduction in the Directed
Haddock Bottom Trawl Fishery,'' and the Council's February 19, 2008,
letter, NMFS is proposing approval of the eliminator trawl. The
pertinent information indicates that the catch of each regulated
species stock of concern, as well as other species, declined by more
than 50 percent with use of the eliminator trawl, which complies with
the first standard for approval of additional gear. The proposed
eliminator trawl net specifications are based upon input from the
individuals involved in the eliminator trawl research, and NMFS gear
experts. Approval of the eliminator trawl would allow trawl vessels
fishing in the Regular B DAS Program or the Eastern U.S./Canada Haddock
SAP a choice of whether to use the haddock separator trawl or the
eliminator trawl. The size of the eliminator trawl specified would be
appropriate for fishing vessels with engines of at least 600
horsepower. The results of the experiment cannot be used to extrapolate
to smaller scale eliminator trawl gear that could be readily used by
smaller horsepower vessels.
The Council identified that the gear performance standards do not
apply to haddock, pollock, and redfish. Haddock, pollock, and redfish
are target stocks for which no reductions in fishing mortality are
required. The researchers could not conduct statistical tests on
Atlantic halibut because the species was not present in sufficient
numbers (defined by the researchers as present in at least 10 paired
tows), and therefore the gear standard could not be applied in a
meaningful way to Atlantic halibut. Because Atlantic halibut is caught
in very low numbers by the trawl fishery, and is subject to a
possession limit of one fish per trip, NMFS has determined that the
lack of information on the compliance of Atlantic halibut with gear
standards is not sufficient justification for disapproval of the
eliminator trawl. Furthermore, it is likely that the selectivity of the
eliminator trawl for Atlantic halibut is low, given the similarity in
body shape and ecology of the Atlantic halibut to the other flatfishes,
which were less numerous in the eliminator trawl. This application of
the gear standard is consistent with the intent of the Council (i.e.,
reasonable flexibility in application of the gear standards) and the
goal of providing opportunities and incentives for the fishing industry
to utilize gear that results in substantial reductions in bycatch.
NMFS is not proposing that vessels must have their eliminator trawl
net inspected and certified by a net manufacturer, as suggested by
Council staff in the attachment to the Council's February 19, 2008,
letter to NMFS. The stated concern is that slight modifications in the
net configuration could alter the effectiveness of the net in reducing
catches of species of concern. Inspection by a net manufacturer would
not prevent a vessel operator from modifying his/her net after such an
inspection occurred, would impose additional costs to the industry,
would be difficult to enforce, and would be redundant, because the net
manufacturer can verify to the net purchaser what he/she is purchasing
at the time of purchase. The fisherman is responsible for the
compliance of his/her gear with the regulations, and NMFS and the
United States Coast Guard enforce the gear regulations. Furthermore,
this requirement was not proposed by the Council (based on the
Council's pertinent motion).
Classification
NMFS has determined that the proposed rule is consistent with the
FMP and has preliminarily determined that this rule is consistent with
the Magnuson-Stevens Fishery Conservation and Management Act and other
applicable laws.
An initial regulatory flexibility analysis (IRFA) has been
prepared, as required by section 603 of the Regulatory Flexibility Act
(RFA), consisting of this proposed rule, the following analysis, and
the Categorical Exclusion prepared for this action. The IRFA below
describes the economic impact this proposed rule, if adopted, would
have on small entities.
Allowing the use of the eliminator trawl in the Regular B DAS
Program and the Eastern U.S./Canada Haddock SAP would provide the
fishing industry more flexibility in the use of trawl gear that
minimizes catch of stocks of concern by providing them with a choice of
whether to use the haddock separator trawl or the eliminator trawl.
Vessels fishing under a Regular B DAS in these programs must comply
with restrictive landing limits of various species. The choice of two
nets would enable a vessel owner to decide which net is the most cost
effective means of targeting haddock and complying with the landing
restrictions. A description of the objectives and legal basis for the
proposed eliminator trawl is contained in the SUMMARY of this proposed
rule.
Under the Small Business Administration (SBA) size standards for
small fishing entities ($ 4.0 million in annual gross sales), all
permitted and participating vessels in the groundfish fishery are
considered to be small entities and, therefore, there are no
disproportionate impacts between large and small entities. Gross sales
by any one entity (vessel) do not exceed this threshold. The maximum
number of small entities that could be affected by the proposed
approval of the eliminator trawl are approximately 1,200 vessels; i.e.,
those issued limited access NE multispecies DAS permits that have an
allocation of Category A or B DAS. Realistically, however, the number
of vessels that choose to fish in either of these programs, and that
would therefore be subject to the associated restrictions, including
the use of either the haddock separator trawl or the eliminator trawl,
would be substantially smaller. For example, in fishing year (FY) 2005,
132 vessels fished in either the Regular B DAS Program or the Eastern
U.S./Canada Haddock SAP. In FY 2006, there were only 45 vessels that
fished in either program. Although it is possible that, under future
circumstances, more vessels may elect to participate in these programs,
a large increase in the numbers of participants is unlikely.
Furthermore, some participants in the Regular B DAS Program and in the
SAP may not have sufficient engine horsepower to use the eliminator
trawl, and, therefore, may not be able to use the trawl.
Based on information from a commercial net manufacturer, the cost
of purchasing a new eliminator trawl net is approximately $ 13,000. A
squid trawl net could be modified into an eliminator trawl for
approximately $ 1,000, by replacing the last belly portion of the net
and putting in a rockhopper sweep. If 130 vessels fished in either of
the special management programs that require the use of a specialized
trawl, and the vessel operators decided to purchase the eliminator
trawl net, the total cost to the industry would be approximately
$1,690,000. It is likely that many vessels that have fished in these
programs in the past using a separator trawl may choose not to purchase
an eliminator trawl. Vessels choosing to use the eliminator trawl would
incur the purchase cost and other
[[Page 29101]]
adjustment costs. The decision to do so, and to thereby fish in a
special management program offering additional revenue opportunities is
a voluntary decision based on the individual vessel's assessment of
profitability.
Because of the context in which this action is proposed, there are
only two alternatives under consideration: The no action alternative
and approval of the eliminator trawl. Consideration of another trawl
gear (i.e., a third alternative) in addition to the eliminator trawl is
not proposed at this time. The process of conducting gear research and
reviewing such research is time consuming and costly, and the standards
for approval must be met. Although other trawl gear research is either
underway or proposed, the eliminator trawl is the only gear that has
been vetted through the review process and recommended by the Council.
Additional research is being proposed by two of the co-authors of
``Bycatch Reduction in the Directed Haddock Bottom Trawl Fishery'' that
will investigate the use of an eliminator trawl net designed for
smaller vessels with 250 to 550 horsepower engines.
Performance standards rather than design standards are utilized for
the evaluation of new trawl gear, in order to provide conservation
engineers flexibility in design and a meaningful standard for the
achievement of the goal of bycatch reduction. The performance standards
under Sec. 648.85(b)(6)(iv)(J)(2) were developed for the specific
purpose of evaluating additional fishing gear for these special
management programs.
The proposed action would not modify any collection of information,
reporting, or recordkeeping requirements. The proposed net does not
duplicate, overlap, or conflict with any other Federal rules.
Dated: May 14, 2008.
John Oliver,
Deputy Assistant Administrator for Operations, National Marine
Fisheries Service.
For the reasons stated in the preamble, 50 CFR part 648 is proposed
to be amended as follows:
PART 648--FISHERIES OF THE NORTHEASTERN UNITED STATES
1. The authority citation for part 648 continues to read as
follows:
Authority: 16 U.S.C. 1801 et seq.
2. In Sec. 648.2, new definitions for ``fishing circle,''
``stretched mesh,'' and ``sweep'' are added in alphabetical order, to
read as follows:
Sec. 648.2 Definitions.
* * * * *
Fishing circle, with respect to the NE multispecies limited access
fishery, means the calculated circumference of a bottom trawl based on
the number of meshes and stretched mesh length at the narrow, aft end
of the square of the net.
* * * * *
Stretched mesh, with respect to the NE multispecies eliminator
trawl, means mesh that is pulled so that slack in the mesh is
eliminated and the mesh opening is closed.
* * * * *
Sweep, with respect to the NE multispecies limited access fishery,
means the part of a bottom trawl that, during normal use, is in contact
with the sea floor along the outer edges of the lower webbing of the
net.
* * * * *
3. In Sec. 648.14, paragraphs (a)(132) and (b)(81) are revised to
read as follows:
Sec. 648.14 Prohibitions.
(a) * * *
(132) If fishing with trawl gear under a NE multispecies DAS in the
Eastern U.S./Canada defined in Sec. 648.85(a)(1)(ii), fail to fish
with a haddock separator trawl or a flounder trawl net, as specified in
Sec. 648.85(a)(3)(iii), unless otherwise allowed under the Eastern
U.S./Canada Haddock SAP rules in Sec. 648.85(b)(8)(v)(E).
* * * * *
(b) * * *
(81) If fishing in the Regular B DAS Program specified in Sec.
648.85(b)(6), fail to use a haddock separator trawl as described under
Sec. 648.85(a)(3)(iii)(A), or other approved gear as described under
Sec. 648.85(b)(6)(iv)(J).
* * * * *
4. In Sec. 648.85, paragraphs (b)(6)(iv)(J)(1) and (b)(8)(v)(E)
introductory heading and (b)(8)(v)(E)(1) are revised, and paragraph
(b)(6)(iv)(J)(3) is added to read as follows:
Sec. 648.85 Special management programs.
* * * * *
(b) * * *
(6) * * *
(iv) * * *
(J) * * *
(1) Vessels fishing with trawl gear in the Regular B DAS Program
must use the haddock separator trawl or eliminator trawl net, as
described under paragraphs (a)(3)(iii)(A) and (b)(6)(iv)(J)(3) of this
section, respectively, or other type of gear if approved as described
under this paragraph (b)(6)(iv)(J). Other gear may be on board the
vessel, provided it is stowed when the vessel is fishing under the
Regular B DAS Program.
* * * * *
(3) Eliminator Trawl. The eliminator trawl is a four-seam bottom
groundfish trawl designed to reduce the bycatch of cod while retaining
or increasing the catch of haddock, when compared to traditional
groundfish trawls. An eliminator trawl must be constructed in
accordance with the following standards:
(i) The net must be constructed with four seams (i.e., a net with a
top and bottom panel and two side panels), and include at least the
following net sections as depicted in Figure 1 of this part
``Nomenclature for 4-seam eliminator trawl'' (this figure is also
available from the Administrator, Northeast Region): Top jib, bottom
jib, jib side panels (x 2), top wing, bottom wing, wing side panels (x
2), square, bunt, square side panels (x 2), first top belly, first
bottom belly, first belly side panels (x 2), second top belly, second
bottom belly, second belly side panels (x 2), and third bottom belly.
(ii) The first bottom belly, bunt, the top and bottom wings, and
the top and bottom jibs, jib side panels, and wing side panels (the
first bottom belly and all portions of the net in front of the first
bottom belly, with the exception of the square and the square side
panels) must be at least two meshes long in the fore and aft direction.
For these net sections the stretched length of any single mesh must be
at least 7.9 ft (240 cm).
(iii) Mesh size in all other sections must be consistent with mesh
size requirements specified under Sec. 648.80 and meet the following
minimum specifications: Each mesh in the square, square side panels,
and second bottom belly must be 31.5 inches (80 cm); each mesh in the
first and second top belly, the first belly side panels, and the third
bottom belly must be at least 7.9 inches (20 cm); and 6 inches or
larger in sections following the second top belly and third bottom
belly sections, all the way to the codend. The mesh size requirements
of the top sections apply to the side panel sections.
(iv) The trawl must have a fishing circle of at least 398 ft (121.4
m). This number is calculated by separately counting the number of
meshes for each section of the net at the wide, fore end of the first
bottom belly, and then calculating a stretched length as follows: For
each section of the net (first bottom belly, two belly side panels and
first top belly) multiply the number of meshes times the length of each
stretched mesh to get the stretched mesh length for that section, and
then add the sections
[[Page 29102]]
together. For example, if the wide, fore end of the bottom belly of the
eliminator trawl is 22 meshes (and the mesh is at least 7.9 ft (240
cm)), the stretched mesh length for that section of the net is derived
by multiplying 22 times 7.9 ft (240 cm) and equals 173.2 ft (52.8 m).
The top and sides (x 2) of the net at this point in the trawl are 343
meshes (221 + 61 + 61, respectively) (each 7.9 inches (20 cm)), which
equals 225.1 ft (68.6 m) stretched length. The stretched lengths for
the different sections of mesh are added together (173.2 ft + 225.1 ft
(52.8 + 68.6 m)) and result in the length of the fishing circle, in
this case 398.3 ft (121.4 m).
(v) The trawl must have at least three 1-square meter or larger
kite panels on the forward end of the square to help maximize headrope
height, for the purpose of capturing rising fish. A kite panel is a
flat structure, usually semi-flexible used to modify the shape of trawl
and mesh openings by providing lift when a trawl is moving through the
water.
(vi) The sweep must consist of rockhoppers, which are graduated
from 16-inch (40-cm) diameter in the center down to 12-inch (30-cm)
diameter at the wing ends. There must be six or fewer 12 to16-inch (30
to 40-cm) rockhopper discs over any 10-ft (3.0 m) length of the sweep.
The 12 to16 inch (30 to 40-cm) discs must be spaced evenly, with one
disc placed approximately every 2 ft (60 cm) along the sweep. The 12 to
16-inch (30 to 40-cm) discs must be separated by smaller discs, no
larger than 3.5 inches (8.8 cm) in diameter.
* * * * *
(8) * * *
(v) * * *
(E) Gear requirement (1) A NE multispecies vessel fishing in the
Eastern U.S./Canada Haddock SAP must use the haddock separator trawl or
eliminator trawl net, as described under paragraphs (a)(3)(iii)(A) and
(b)(6)(iv)(J)(3) of this section, respectively, or other type of gear,
if approved as described under this paragraph (b)(8)(v)(E). No other
type of fishing gear may be on the vessel when on a trip in the Eastern
U.S./Canada Haddock SAP, with the exception of a flounder net, as
described in paragraph (a)(3)(iii) of this section, provided that the
flounder net is stowed in accordance with Sec. 648.23(b).
* * * * *
5. In part 648, add Figure 1 as follows:
BILLING CODE 3510-22-S
[[Page 29103]]
[GRAPHIC] [TIFF OMITTED] TP20MY08.015
[FR Doc. E8-11303 Filed 5-19-08; 8:45 am]
BILLING CODE 3510-22-C