[Federal Register Volume 76, Number 251 (Friday, December 30, 2011)]
[Rules and Regulations]
[Pages 82183-82189]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2011-33300]


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DEPARTMENT OF COMMERCE

National Oceanic and Atmospheric Administration

50 CFR Part 622

[Docket No. 110831547-1736-02]
RIN 0648-BB26


Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic; 
Comprehensive Ecosystem-Based Amendment 2 for the South Atlantic Region

AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and

[[Page 82184]]

Atmospheric Administration (NOAA), Commerce.

ACTION: Final rule.

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SUMMARY: NMFS issues this final rule to implement the Comprehensive 
Ecosystem-Based Amendment 2 (CE-BA 2) to implement the following South 
Atlantic fishery management plan (FMP) amendments: Amendment 1 to the 
FMP for Pelagic Sargassum Habitat of the South Atlantic Region 
(Sargassum FMP); Amendment 7 to the FMP for Coral, Coral reefs, and 
Live/Hard Bottom Habitats of the South Atlantic Region (Coral FMP); and 
Amendment 25 to the FMP for the Snapper-Grouper Fishery of the South 
Atlantic Region (Snapper-Grouper FMP), as prepared and submitted by the 
South Atlantic Fishery Management Council (Council); as well as 
Amendment 21 to the FMP for Coastal Migratory Pelagic (CMP) Resources 
(CMP FMP) as prepared and submitted by the South Atlantic and Gulf of 
Mexico Fishery Management Councils. This rule modifies the fishery 
management unit (FMU) for octocorals in the South Atlantic exclusive 
economic zone (EEZ), establishes an annual catch limit (ACL) for 
octocorals, modifies management in special management zones (SMZs) off 
South Carolina, and modifies sea turtle and smalltooth sawfish release 
gear specifications in the South Atlantic region. CE-BA 2 also 
designates new Essential Fish Habitat (EFH) for Sargassum, and EFH-
Habitat Areas of Particular Concern (EFH-HAPCs) for the Snapper-
Grouper, Coral FMPs. This rule specifies ACLs for species not 
undergoing overfishing (octocorals), implements management measures to 
ensure overfishing does not occur for these species but optimum yield 
may be achieved, and conserves and protects habitat in the South 
Atlantic region.

DATES: This rule is effective January 30, 2012.

ADDRESSES: Electronic copies of the amendment, which includes an 
environmental impact statement, a regulatory impact review, and the 
initial regulatory flexibility analysis (IRFA), may be obtained from 
the Southeast Regional Office Web site at http://sero.nmfs.noaa.gov/sf/SACoralandCoralReefs.htm.

FOR FURTHER INFORMATION CONTACT: Karla Gore, Southeast Regional Office, 
NMFS, telephone: (727) 824-5305, email: [email protected].

SUPPLEMENTARY INFORMATION: The fisheries for CMP species; coral, coral 
reefs, and live/hard bottom habitats; pelagic Sargassum; and snapper-
grouper off the southern Atlantic states are managed under their 
respective FMPs. The FMPs were prepared by the Council(s) and are 
implemented under the authority of the Magnuson-Stevens Fishery 
Conservation and Management Act (Magnuson-Stevens Act) by regulations 
at 50 CFR part 622.
    On September 26, 2011, NMFS published a notice of availability for 
CE-BA 2 and requested public comment (76 FR 59371). On November 8, 
2011, NMFS published a proposed rule for CE-BA 2 and requested public 
comment (76 FR 69230). The proposed rule and CE-BA 2 outline the 
rationale for the actions contained in this final rule. A summary of 
the actions implemented by this final rule are provided below.
    This rule modifies the FMU for octocorals under the Coral FMP to 
include octocorals in the EEZ off North Carolina, South Carolina, and 
Georgia only. Federal management of octocorals in the EEZ off Florida 
is no longer included under the Coral FMP. Florida's Fish and Wildlife 
Conservation Commission (FWC) is currently responsible for the majority 
of the management, implementation, and enforcement of octocorals, 
because the majority of octocoral harvest occurs in Florida state 
waters. The FWC intends to extend management of octocorals into Federal 
waters off Florida.
    This rule specifies an ACL of zero for octocorals in the South 
Atlantic EEZ. Prior to implementation of this final rule, a 50,000 
colony quota for octocorals was in place in the Gulf of Mexico (Gulf) 
and South Atlantic regions and a prohibition was in effect to harvest 
octocorals north of Florida. Florida has implemented regulations 
compatible to the applicable Federal regulations, which allow the state 
octocoral fishery to close when the Federal quota is met. Because the 
majority of octocoral harvest occurs in state waters off Florida and 
the prohibition on the harvest of octocorals north of Florida would 
continue, the Council voted to remove octocorals off Florida from the 
FMU and establish an ACL of zero for octocorals off Georgia, South 
Carolina, and North Carolina.
    This final rule limits the harvest and possession of South Atlantic 
snapper-grouper species and CMP species (with the use of all non-
prohibited fishing gear) in the SMZs off South Carolina to the 
recreational bag limit. This rule prohibits fishermen from harvesting 
commercial quantities of snapper-grouper and CMP in these SMZs.
    This final rule also modifies the sea turtle and smalltooth sawfish 
release gear requirements. The sea turtle and smalltooth sawfish 
release gear requirements are revised based on the freeboard height of 
the vessels to provide flexibility to fisherman based on their vessel 
characteristics.
    CE-BA 2 also amends South Atlantic FMPs as needed to designate new 
EFH and EFH-HAPCs. CE-BA 2 amends the Snapper-Grouper FMP to designate 
deepwater marine protected areas (MPAs) as EFH-HAPCs. The Coral FMP is 
amended to designate deep-water coral HAPCs as EFH-HAPCs. To meet the 
Magnuson-Stevens Act requirement that all federally managed species 
have EFH designated, CE-BA 2 amends the Sargassum FMP to designate the 
top 33 ft (10 m) of the water column in the South Atlantic EEZ bounded 
by the Gulf Stream, as EFH for pelagic Sargassum. The addition of this 
information does not require any changes in regulatory language.

Comments and Responses

    NMFS received two comment letters with a total of five separate 
comments, on CE-BA 2 and the proposed rule. One comment letter was in 
support of the actions in CE-BA 2. The other comment letter, from an 
industry group, restated their previous recommendations made to the 
Council regarding the actions in CE-BA 2. Comments related to the 
actions contained in the amendment or the proposed rule are summarized 
and responded to below.
    Comment 1: One commenter supports the actions to modify management 
in the SMZs of South Carolina, establish EFH-HAPCs for the snapper-
grouper fishery, and establish EFH for the Sargassum fishery.
    Response: NMFS concurs and believes that these actions are 
consistent with the Magnuson-Stevens Act and CE-BA 2.
    Comment 2: One commenter supports retaining Florida octocorals in 
the FMU, the 50,000 colony octocoral quota, and extending octocoral 
management into the Gulf.
    Response: The commenter did not provide any rationale for the 
recommendations submitted, and the comments were previously submitted 
to the Council before the current preferred alternatives were selected. 
The Council recommended revising the FMU for the Coral FMP to include 
only octocorals off Georgia, North Carolina, and South Carolina because 
the need for Federal conservation and management off Florida no longer 
exists. The FWC is responsible for most of the management, 
implementation, and enforcement of octocorals because the majority of 
the harvest occurs in Florida state waters, and the Federal quota has 
never been reached. In a letter dated April 11, 2011, the FWC describes 
octocoral

[[Page 82185]]

management measures it would implement if the Federal FMU is modified 
to remove the octocorals off Florida. According to the FWC letter, the 
FWC intends to extend Florida octocoral regulations into the Federal 
waters off Florida (Gulf and South Atlantic), to establish an annual 
quota of 70,000 colonies for allowable octocoral harvest in state and 
Federal waters combined off Florida, and to prohibit the harvest of 
octocorals in Florida waters north of Cape Canaveral, Florida and in 
the Coral HAPCs off Florida. The Gulf Fishery Management Council has 
also recommended removing octocorals in the Gulf off Florida from their 
FMU within the FMP for Coral and Coral Reefs of the Gulf for 
consistency of management.
    In addition, the Council recommended the establishment of an ACL 
equal to zero for octocorals off South Carolina, North Carolina, and 
Georgia in the revised FMU. Functionally, this would not have any 
impact on active octocoral harvesters as there has been a prohibition 
on octocoral harvest north of Cape Canaveral, Florida since 1995. Under 
this scenario, management of octocorals off Florida would continue to 
be managed by the FWC.
    Comment 3: One commenter recommended that the Council select 
Alternative 5, which modifies the design specifications of the current 
sea turtle release gear requirements to allow for more appropriate gear 
with respect to the lighter tackle used by snapper-grouper fishermen.
    Response: The Council selected Alternative 4, and associated sub-
alternatives 4a and 4b as the Preferred Alternative for the action to 
have the sea turtle release gear requirements dependent on vessel 
freeboard height, to accommodate both smaller vessels using lighter 
tackle to harvest snapper-grouper species (vessels with a freeboard 
height of 4 ft (1.2 m) or less) and larger vessels using heavier gear 
(vessels with a freeboard height of 4 ft (1.2 m) or more). This 
Preferred Alternative is consistent with the requirements of the June 
7, 2006, Biological Opinion on the Snapper-Grouper Fishery and responds 
to the concerns of fishermen that sea turtle handling gear are unwieldy 
and inappropriate for all vessel sizes. While Alternative 5, and 
associated sub-alternatives, may also be consistent with the biological 
opinion, the Council sought to maximize biological benefits by allowing 
sea turtle release gear that is more appropriate to a particular 
vessel. Alternative 4, and associated sub-alternatives, is also 
consistent with sea turtle release gear requirements in the Gulf, and 
simplifies requirements for fishermen participating in both fisheries.
    Comment 4: One commenter supports the alternative that would not 
designate new EFH-HAPCs in the Coral FMP and would allow the existing 
designations to remain in effect.
    Response: The commenter provided no rationale for its 
recommendation. The establishment of EFH and EFH-HAPCs requires that 
further consideration be given to fishing and non-fishing activities 
that occur in these areas. However, in itself, the establishment of EFH 
and EFH-HAPCs does not modify Federal fishery regulations in any way. 
The Council and NMFS also expect that the establishment of the EFH and 
EFH-HAPCs will benefit ocean and coastal habitats in the future through 
the EFH consultation process. Through that process, the Council will be 
in a better position to evaluate whether further protections are 
necessary.
    Comment 5: One commenter does not support the establishment of EFH-
HAPCs for Sargassum.
    Response: In March 2011, the Council decided to remove this action 
from consideration within CE-BA 2 because the areas proposed for this 
designation (the Charleston Bump Complex, and The Point, NC) were 
already designated as EFH-HAPCs for snapper-grouper and dolphin and 
wahoo, and conservation of these specific EFH-HAPCs would be addressed 
through actions associated with EFH consultations pertaining to 
existing EFH-HAPC designations. Therefore, EFH for Sargassum is 
designated as the top 33 ft (10 m) of the water column in the South 
Atlantic EEZ bounded by the Gulfstream, but no EFH-HAPCs were 
designated for Sargassum in CE-BA 2.

Classification

    The Regional Administrator, Southeast Region, NMFS has determined 
that this final rule is necessary for the conservation and management 
of the species within CE-BA 2 and is consistent with the Magnuson-
Stevens Act, and other applicable law.
    This final rule has been determined to be not significant for 
purposes of Executive Order 12866.
    NMFS prepared an IRFA for the proposed rule that described the 
economic impact of the rule. As described in the IRFA, the only action 
in this rule that may have any direct adverse economic effect on the 
profits of any small entities is the limitation on harvest of snapper-
grouper and CMP species in the SMZs off South Carolina to the 
recreational bag limit. Because data on the number of commercial 
vessels that fish in these SMZs, and the associated harvest, is not 
available at sufficient spatial resolution to quantitatively assess the 
impacts of the action, it is not possible to determine if the reduction 
in profits for any small entities would be significant. However, based 
on tabulation of the number of appropriate commercial permits in nearby 
coastal areas, the IRFA determined that the number of affected vessels 
would encompass at most approximately 4 percent of South Atlantic 
vessels with king mackerel permits, 2 percent of South Atlantic vessels 
with Spanish mackerel permits (king mackerel and Spanish mackerel 
permits allow fishing in both the Gulf and South Atlantic and, because 
of the narrow geographic applicability this action, only counts for 
permits with homeport addresses in the South Atlantic were included in 
the assessment), and 9 percent of vessels with snapper-grouper permits. 
Additionally, because the problem of commercial harvest in the SMZs is 
believed to be mostly limited to vessels using spear gear (hand spear 
or spear guns), which is not the dominant gear type used to harvest 
these species, substantially fewer vessels than these maximum amounts 
would be expected to be affected. As a result, only a small number of 
vessels in the CMP and snapper-grouper fleets would be expected to be 
directly affected by this rule. Because of this finding, the IRFA 
concluded that the actions in this rule would not be expected to 
significantly reduce profits for a substantial number of small 
entities. Nevertheless, because of the lack of data on vessels that 
historically harvest commercial quantities of these species from these 
areas, public comment was requested on this determination and a 
certification was not prepared. No comments were received regarding the 
determination. Therefore, NMFS concluded that the determination was 
correct and the Chief Counsel for Regulation of the Department of 
Commerce has certified to the Chief Counsel for Advocacy of the Small 
Business Administration at this stage in the rulemaking that this 
action will not have a significant economic impact on a substantial 
number of small entities. As a result, a final regulatory flexibility 
analysis was not required and none was prepared.

List of Subjects in 50 CFR Part 622

    Fisheries, Fishing, Puerto Rico, Reporting and recordkeeping 
requirements, Virgin Islands.


[[Page 82186]]


    Dated: December 22, 2011.
Samuel D. Rauch III,
Deputy Assistant Administrator for Regulatory Programs, National Marine 
Fisheries Service.
    For the reasons set out in the preamble, 50 CFR part 622 is amended 
as follows:

PART 622--FISHERIES OF THE CARIBBEAN, GULF, AND SOUTH ATLANTIC

0
1. The authority citation for part 622 continues to read as follows:

    Authority:  16 U.S.C. 1801 et seq.

0
2. In Sec.  622.1, paragraph (b), Table 1, the entry for ``FMP for 
Coral, Coral Reefs, and Live/Hard Bottom Habitats of the South Atlantic 
Region'' is revised and footnote 7 is added to read as follows:


Sec.  622.1  Purpose and scope.

* * * * *
    (b) * * *

                                    Table 1--FMPs Implemented Under Part 622
----------------------------------------------------------------------------------------------------------------
                                                Responsible fishery
                FMP title                     management  council(s)                Geographical area
----------------------------------------------------------------------------------------------------------------
 
                                                  * * * * * * *
FMP for Coral, Coral Reefs, and Live/Hard  SAFMC.......................  South Atlantic.\7\
 Bottom Habitats of the South Atlantic
 Region.
 
                                                  * * * * * * *
----------------------------------------------------------------------------------------------------------------
\7\ Octocorals are managed by the FMP or regulated by this part only in the EEZ off North Carolina, South
  Carolina, and Georgia.

* * * * *

0
2. In Sec.  622.10, paragraphs (c)(1)(ii) and (iii), are revised to 
read as follows:


Sec.  622.10  Conservation measures for protected resources.

* * * * *
    (c) * * *
    (1) * * *
    (ii) Such owner or operator must also comply with the sea turtle 
bycatch mitigation measures, including gear requirements and sea turtle 
handling requirements, specified in Appendix E to this part.
    (iii) Those permitted vessels with a freeboard height of 4 ft (1.2 
m) or less must have on board and must use a dipnet, cushioned/support 
device, short-handled dehooker, long-nose or needle-nose pliers, bolt 
cutters, monofilament line cutters, and at least two types of mouth 
openers/mouth gags. This equipment must meet the specifications 
described in Appendix E to this part. Those permitted vessels with a 
freeboard height of greater than 4 ft (1.2 m) must have on board a 
dipnet, cushioned/support device, long-handled line clipper, a short-
handled and a long-handled dehooker, a long-handled device to pull an 
inverted ``V'', long-nose or needle-nose pliers, bolt cutters, 
monofilament line cutters, and at least two types of mouth openers/
mouth gags. This equipment must meet the specifications described in 
Appendix E to this part.
* * * * *

0
3. In Sec.  622.32, paragraph (b)(3)(viii) is added to read as follows:


Sec.  622.32  Prohibited and limited harvest species.

* * * * *
    (b) * * *
    (3) * * *
    (viii) Octocoral may not be harvested or possessed in or from the 
portion of the South Atlantic EEZ managed under the FMP. Octocoral 
collected in the portion of the South Atlantic EEZ managed under the 
FMP must be released immediately with a minimum of harm.
* * * * *

0
4. In Sec.  622.35, in paragraph (e)(2), the first entry in the table 
is revised to read as follows:


Sec.  622.35  Atlantic EEZ seasonal and/or area closures.

* * * * *
    (e) * * *
    (2) * * *

------------------------------------------------------------------------
In SMZs Specified in the following
    paragraphs of Sec.   622.35           These restrictions apply
------------------------------------------------------------------------
(e)(1)(i) through (x), (e)(1)(xx),  Use of a powerhead to take South
 and (e)(1)(xxii) through (xxxix).   Atlantic snapper-grouper is
                                     prohibited. Possession of a
                                     powerhead and a mutilated South
                                     Atlantic snapper-grouper in, or
                                     after having fished in, one of
                                     these SMZs constitutes prima facie
                                     evidence that such fish was taken
                                     with a powerhead in the SMZ.
                                     Harvest and possession of a coastal
                                     migratory pelagic fish or a South
                                     Atlantic snapper-grouper is limited
                                     to the bag-limits specified in Sec.
                                       622.39(c)(1) and (d)(1),
                                     respectively.
 
                              * * * * * * *
------------------------------------------------------------------------


0
5. In Sec.  622.42, paragraph (b) is revised to read as follows:


Sec.  622.42  Quotas.

* * * * *
    (b) Gulf allowable octocoral. The quota for all persons who harvest 
allowable octocoral in the Gulf EEZ is 50,000 colonies. A colony is a 
continuous group of coral polyps forming a single unit.
* * * * *

0
6. Appendix E is added to part 622 to read as follows:

Appendix E to Part 622--Specifications for Sea Turtle Mitigation Gear 
and Sea Turtle Handling and Release Requirements

    A. Sea turtle mitigation gear.
    1. Long-handled line clipper or cutter. Line cutters are 
intended to cut high test monofilament line as close as possible to 
the hook, and assist in removing line from entangled sea turtles to 
minimize any

[[Page 82187]]

remaining gear upon release. NMFS has established minimum design 
standards for the line cutters. The LaForce line cutter and the 
Arceneaux line clipper are models that meet these minimum design 
standards, and may be purchased or fabricated from readily available 
and low-cost materials. One long-handled line clipper or cutter and 
a set of replacement blades are required to be onboard. The minimum 
design standards for line cutters are as follows:
    (a) A protected and secured cutting blade. The cutting blade(s) 
must be capable of cutting 2.0-2.1 mm (0.078 in.-0.083 in.) 
monofilament line (400-lb test) or polypropylene multistrand 
material, known as braided or tarred mainline, and must be 
maintained in working order. The cutting blade must be curved, 
recessed, contained in a holder, or otherwise designed to facilitate 
its safe use so that direct contact between the cutting surface and 
the sea turtle or the user is prevented. The cutting instrument must 
be securely attached to an extended reach handle and be easily 
replaceable. One extra set of replacement blades meeting these 
standards must also be carried on board to replace all cutting 
surfaces on the line cutter or clipper.
    (b) An extended reach handle. The line cutter blade must be 
securely fastened to an extended reach handle or pole with a minimum 
length equal to, or greater than, 150 percent of the freeboard, or a 
minimum of 6 ft (1.83 m), whichever is greater. It is recommended, 
but not required, that the handle break down into sections. There is 
no restriction on the type of material used to construct this handle 
as long as it is sturdy and facilitates the secure attachment of the 
cutting blade.
    2. Long-handled dehooker for internal hooks. A long-handled 
dehooking device is intended to remove internal hooks from sea 
turtles that cannot be boated. It should also be used to engage a 
loose hook when a turtle is entangled but not hooked, and line is 
being removed. The design must shield the barb of the hook and 
prevent it from re-engaging during the removal process. One long-
handled device to remove internal hooks is required onboard. The 
minimum design standards are as follows:
    (a) Hook removal device. The hook removal device must be 
constructed of approximately \3/16\-inch (4.76 mm) to \5/16\-inch 
(7.94 mm) 316 L stainless steel or similar material and have a 
dehooking end no larger than 1\7/8\-inches (4.76 cm) outside 
diameter. The device must securely engage and control the leader 
while shielding the barb to prevent the hook from re-engaging during 
removal. It may not have any unprotected terminal points (including 
blunt ones), as these could cause injury to the esophagus during 
hook removal. The device must be of a size appropriate to secure the 
range of hook sizes and styles used in the South Atlantic snapper-
grouper fishery.
    (b) Extended reach handle. The dehooking end must be securely 
fastened to an extended reach handle or pole with a minimum length 
equal to or greater than 150 percent of the freeboard, or a minimum 
of 6 ft (1.83 m), whichever is greater. It is recommended, but not 
required, that the handle break down into sections. The handle must 
be sturdy and strong enough to facilitate the secure attachment of 
the hook removal device.
    3. Long-handled dehooker for external hooks. A long-handled 
dehooker is required for use on externally-hooked sea turtles that 
cannot be boated. The long-handled dehooker for internal hooks 
described in paragraph 2. of this Appendix E would meet this 
requirement. The minimum design standards are as follows:
    (a) Construction. A long-handled dehooker must be constructed of 
approximately \3/16\-inch (4.76 mm) to \5/16\-inch (7.94 mm) 316 L 
stainless steel rod and have a dehooking end no larger than 1\7/8\-
inches (4.76 cm) outside diameter. The design should be such that a 
fish hook can be rotated out, without pulling it out at an angle. 
The dehooking end must be blunt with all edges rounded. The device 
must be of a size appropriate to secure the range of hook sizes and 
styles used in the South Atlantic snapper-grouper fishery.
    (b) Extended reach handle. The handle must be a minimum length 
equal to the freeboard of the vessel or 6 ft (1.83 m), whichever is 
greater.
    4. Long-handled device to pull an ``inverted V''. This tool is 
used to pull a ``V'' in the fishing line when implementing the 
``inverted V'' dehooking technique, as described in the document 
entitled ``Careful Release Protocols for Sea Turtle Release With 
Minimal Injury,'' for disentangling and dehooking entangled sea 
turtles. One long-handled device to pull an ``inverted V'' is 
required onboard. If a 6-ft (1.83 m) J-style dehooker is used to 
comply with paragraph 4. of this Appendix E, it will also satisfy 
this requirement. Minimum design standards are as follows:
    (a) Hook end. This device, such as a standard boat hook, gaff, 
or long-handled J-style dehooker, must be constructed of stainless 
steel or aluminum. The semicircular or ``J'' shaped end must be 
securely attached to a handle. A sharp point, such as on a gaff 
hook, is to be used only for holding the monofilament fishing line 
and should never contact the sea turtle.
    (b) Extended reach handle. The handle must have a minimum length 
equal to the freeboard of the vessel, or 6 ft (1.83 m), whichever is 
greater. The handle must be sturdy and strong enough to facilitate 
the secure attachment of the gaff hook.
    5. Dipnet. One dipnet is required onboard. Dipnets are to be 
used to facilitate safe handling of sea turtles by allowing them to 
be brought onboard for fishing gear removal, without causing further 
injury to the animal. Turtles must not be brought onboard without 
the use of a dipnet or hoist. The minimum design standards for 
dipnets are as follows:
    (a) Size of dipnet. The dipnet must have a sturdy net hoop of at 
least 31 inches (78.74 cm) inside diameter and a bag depth of at 
least 38 inches (96.52 cm) to accommodate turtles below 3 ft (0.914 
m) carapace length. The bag mesh openings may not exceed 3 inches 
(7.62 cm) by 3 inches (7.62 cm). There must be no sharp edges or 
burrs on the hoop, or where it is attached to the handle. There is 
no requirement for the hoop to be circular as long as it meets the 
minimum specifications.
    (b) Extended reach handle. The dipnet hoop must be securely 
fastened to an extended reach handle or pole with a minimum length 
equal to, or greater than, 150 percent of the freeboard, or at least 
6 ft (1.83 m), whichever is greater. The handle must be made of a 
rigid material strong enough to facilitate the sturdy attachment of 
the net hoop and be able to support a minimum of 100 lb (34.1 kg) 
without breaking or significant bending or distortion. It is 
recommended, but not required, that the extended reach handle break 
down into sections.
    6. Cushion/support device. A standard automobile tire (free of 
exposed steel belts), a boat cushion, a large turtle hoist, or any 
other comparable cushioned elevated surface, is required for 
supporting a turtle in an upright orientation while the turtle is 
onboard. The cushion/support device must be appropriately sized to 
fully support a range of turtle sizes.
    7. Short-handled dehooker for internal hooks. One short-handled 
device for removing internal hooks is required onboard. This 
dehooker is designed to remove ingested hooks from boated sea 
turtles. It can also be used on external hooks or hooks in the front 
of the mouth. Minimum design standards are as follows:
    (a) Hook removal device. The hook removal device must be 
constructed of approximately \3/16\-inch (4.76 mm) to \5/16\-inch 
(7.94 mm) 316 L stainless steel, and must allow the hook to be 
secured and the barb shielded without re-engaging during the removal 
process. It must be no larger than 1\7/8\-inches (4.76 cm) outside 
diameter. It may not have any unprotected terminal points (including 
blunt ones), as this could cause injury to the esophagus during hook 
removal. A sliding PVC bite block must be used to protect the beak 
and facilitate hook removal if the turtle bites down on the 
dehooking device. The bite block should be constructed of a \3/4\-
inch (1.91 cm) inside diameter high impact plastic cylinder (e.g., 
Schedule 80 PVC) that is 4 to 6 inches (10.2 to 15.2 cm) long to 
allow for 5 inches (12.7 cm) of slide along the shaft. The device 
must be of a size appropriate to secure the range of hook sizes and 
styles used in the South Atlantic snapper-grouper fishery.
    (b) Handle length. The handle should be approximately 16 to 24 
inches (40.64 cm to 60.69 cm) in length, with approximately a 4 to 
6-inch (10.2 to 15.2-cm) long tube T-handle of approximately 1 inch 
(2.54 cm) in diameter.
    8. Short-handled dehooker for external hooks. One short-handled 
dehooker for external hooks is required onboard. The short-handled 
dehooker for internal hooks required to comply with paragraph 7. of 
this Appendix E will also satisfy this requirement. Minimum design 
standards are as follows:
    (a) Hook removal device. The dehooker must be constructed of 
approximately \3/16\-inch (4.76 cm) to \5/16\-inch (7.94 cm) 316 L 
stainless steel, and the design must be such that a hook can be 
rotated out without pulling it out at an angle. The dehooking end 
must be blunt, and all edges rounded. The device must be of a size 
appropriate to secure the range of hook sizes and styles used in the 
South Atlantic snapper-grouper fishery.

[[Page 82188]]

    (b) Handle length. The handle should be approximately 16 to 24 
inches (40.64 to 60.69 cm) long with approximately a 5-inch (12.7 
cm) long tube T-handle, wire loop handle or similar, of 
approximately 1 inch (2.54 cm) in diameter.
    9. Long-nose or needle-nose pliers. One pair of long-nose or 
needle-nose pliers is required on board. Required long-nose or 
needle-nose pliers can be used to remove deeply embedded hooks from 
the turtle's flesh that must be twisted during removal or for 
removing hooks from the front of the mouth. They can also hold PVC 
splice couplings, when used as mouth openers, in place. Minimum 
design standards are as follows:
    (a) General. They must be approximately 12 inches (30.48 cm) in 
length, and should be constructed of stainless steel material.
    (b) [Reserved]
    10. Bolt cutters. One pair of bolt cutters is required on board. 
Required bolt cutters may be used to cut hooks to facilitate their 
removal. They should be used to cut off the eye or barb of a hook, 
so that it can safely be pushed through a sea turtle without causing 
further injury. They should also be used to cut off as much of the 
hook as possible, when the remainder of the hook cannot be removed. 
Minimum design standards are as follows:
    (a) General. They must be approximately 14 to 17 inches (35.56 
to 43.18 cm) in total length, with approximately 4-inch (10.16 cm) 
long blades that are 2\1/4\ inches (5.72 cm) wide, when closed, and 
with approximately 10 to 13-inch (25.4 to 33.02-cm) long handles. 
Required bolt cutters must be able to cut hard metals, such as 
stainless or carbon steel hooks, up to 1/4-inch (6.35 mm) diameter.
    (b) [Reserved]
    11. Monofilament line cutters. One pair of monofilament line 
cutters is required on board. Required monofilament line cutters 
must be used to remove fishing line as close to the eye of the hook 
as possible, if the hook is swallowed or cannot be removed. Minimum 
design standards are as follows:
    (a) General. Monofilament line cutters must be approximately 
7\1/2\ inches (19.05 cm) in length. The blades must be 1 inch (4.45 
cm) in length and \5/8\ inches (1.59 cm) wide, when closed.
    (b) [Reserved]
    12. Mouth openers/mouth gags. Required mouth openers and mouth 
gags are used to open sea turtle mouths, and to keep them open when 
removing internal hooks from boated turtles. They must allow access 
to the hook or line without causing further injury to the turtle. 
Design standards are included in the item descriptions. At least two 
of the seven different types of mouth openers/gags described below 
are required:
    (a) A block of hard wood. Placed in the corner of the jaw, a 
block of hard wood may be used to gag open a turtle's mouth. A 
smooth block of hard wood of a type that does not splinter (e.g. 
maple) with rounded edges should be sanded smooth, if necessary, and 
soaked in water to soften the wood. The dimensions should be 
approximately 11 inches (27.94 cm) by 1 inch (2.54 cm) by 1 inch 
(2.54 cm). A long-handled, wire shoe brush with a wooden handle, and 
with the wires removed, is an inexpensive, effective and practical 
mouth-opening device that meets these requirements.
    (b) A set of three canine mouth gags. Canine mouth gags are 
highly recommended to hold a turtle's mouth open, because the gag 
locks into an open position to allow for hands-free operation after 
it is in place. These tools are only for use on small and medium 
sized turtles, as larger turtles may be able to crush the mouth gag. 
A set of canine mouth gags must include one of each of the following 
sizes: Small (5 inches) (12.7 cm), medium (6 inches) (15.24 cm), and 
large (7 inches) (17.78 cm). They must be constructed of stainless 
steel. The ends must be covered with clear vinyl tubing, friction 
tape, or similar, to pad the surface.
    (c) A set of two sturdy dog chew bones. Placed in the corner of 
a turtle's jaw, canine chew bones are used to gag open a sea 
turtle's mouth. Required canine chews must be constructed of durable 
nylon, zylene resin, or thermoplastic polymer, and strong enough to 
withstand biting without splintering. To accommodate a variety of 
turtle beak sizes, a set must include one large (5\1/2\-8 inches 
(13.97 cm-20.32 cm) in length), and one small (3\1/2\-4\1/2\ inches 
(8.89 cm-11.43 cm) in length) canine chew bones.
    (d) A set of two rope loops covered with protective tubing. A 
set of two pieces of poly braid rope covered with light duty garden 
hose or similar flexible tubing each tied or spliced into a loop to 
provide a one-handed method for keeping the turtle's mouth open 
during hook and/or line removal. A required set consists of two 3-ft 
(0.91 m) lengths of poly braid rope (\3/8\-inch (9.52 mm) diameter 
suggested), each covered with an 8-inch (20.32 cm) section of \1/2\ 
inch (1.27 cm) or \3/4\ inch (1.91 cm) tubing, and each tied into a 
loop. The upper loop of rope covered with hose is secured on the 
upper beak to give control with one hand, and the second piece of 
rope covered with hose is secured on the lower beak to give control 
with the user's foot.
    (e) A hank of rope. Placed in the corner of a turtle's jaw, a 
hank of rope can be used to gag open a sea turtle's mouth. A 6-ft 
(1.83 m) lanyard of approximately \3/16\-inch (4.76 mm) braided 
nylon rope may be folded to create a hank, or looped bundle, of 
rope. Any size soft-braided nylon rope is allowed, however it must 
create a hank of approximately 2-4 inches (5.08 cm-10.16 cm) in 
thickness.
    (f) A set of four PVC splice couplings. PVC splice couplings can 
be positioned inside a turtle's mouth to allow access to the back of 
the mouth for hook and line removal. They are to be held in place 
with the needle-nose pliers. To ensure proper fit and access, a 
required set must consist of the following Schedule 40 PVC splice 
coupling sizes: 1 inch (2.54 cm), 1\1/4\ inch (3.18 cm), 1\1/2\ inch 
(3.81 cm), and 2 inches (5.08 cm).
    (g) A large avian oral speculum. A large avian oral speculum 
provides the ability to hold a turtle's mouth open and to control 
the head with one hand, while removing a hook with the other hand. 
The avian oral speculum must be 9-inches (22.86 cm) long, and 
constructed of \3/16\-inch (4.76 mm) wire diameter surgical 
stainless steel (Type 304). It must be covered with 8 inches (20.32 
cm) of clear vinyl tubing (\5/16\-inch (7.9 mm) outside diameter, 
\3/16\-inch (4.76 mm) inside diameter), friction tape, or similar to 
pad the surface.
    B. Sea turtle handling and release requirements. Sea turtle 
bycatch mitigation gear, as specified in paragraphs A.1. through 4. 
of this Appendix E, must be used to disengage any hooked or 
entangled sea turtles that cannot be brought onboard. Sea turtle 
bycatch mitigation gear, as specified in paragraphs A.5. through 12. 
of this Appendix E, must be used to facilitate access, safe 
handling, disentanglement, and hook removal or hook cutting of sea 
turtles that can be brought onboard, where feasible. Sea turtles 
must be handled, and bycatch mitigation gear must be used, in 
accordance with the careful release protocols and handling/release 
guidelines specified in Sec.  622.10(c)(1), and in accordance with 
the onboard handling and resuscitation requirements specified in 
Sec.  223.206(d)(1) of this title.
    1. Boated turtles. When practicable, active and comatose sea 
turtles must be brought on board, with a minimum of injury, using a 
dipnet as specified in paragraph A.5. of this Appendix E. All 
turtles less than 3 ft (.91 m) carapace length should be boated, if 
sea conditions permit.
    (a) A boated turtle should be placed on a cushioned/support 
device, as specified in paragraph A.6. of this Appendix E, in an 
upright orientation to immobilize it and facilitate gear removal. 
Then, it should be determined if the hook can be removed without 
causing further injury. All externally embedded hooks should be 
removed, unless hook removal would result in further injury to the 
turtle. No attempt to remove a hook should be made if it has been 
swallowed and the insertion point is not visible, or if it is 
determined that removal would result in further injury. If a hook 
cannot be removed, as much line as possible should be removed from 
the turtle using monofilament cutters as specified in paragraph 
A.11. of this Appendix E, and the hook should be cut as close as 
possible to the insertion point before releasing the turtle, using 
bolt cutters as specified in paragraph A.10. of this Appendix E. If 
a hook can be removed, an effective technique may be to cut off 
either the barb, or the eye, of the hook using bolt cutters, and 
then to slide the hook out. When the hook is visible in the front of 
the mouth, a mouth-opener, as specified in paragraph A.12. of this 
Appendix E, may facilitate opening the turtle's mouth and a gag may 
facilitate keeping the mouth open. Short-handled dehookers for 
internal hooks, or long-nose or needle-nose pliers, as specified in 
paragraphs A.7. and A.8. of this Appendix E, respectively, should be 
used to remove visible hooks from the mouth that have not been 
swallowed on boated turtles, as appropriate. As much gear as 
possible must be removed from the turtle without causing further 
injury prior to its release. Refer to the careful release protocols 
and handling/release guidelines required in Sec.  622.10(c)(1), and 
the handling and resuscitation requirements specified in Sec.  
223.206(d)(1) of this title, for additional information.

[[Page 82189]]

    (b) [Reserved]
    2. Non-boated turtles. If a sea turtle is too large, or hooked 
in a manner that precludes safe boating without causing further 
damage or injury to the turtle, sea turtle bycatch mitigation gear 
specified in paragraphs A.1. through 4. of this Appendix E must be 
used to disentangle sea turtles from fishing gear and disengage any 
hooks, or to clip the line and remove as much line as possible from 
a hook that cannot be removed, prior to releasing the turtle, in 
accordance with the protocols specified in Sec.  622.10(c)(1).
    (a) Non-boated turtles should be brought close to the boat and 
provided with time to calm down. Then, it must be determined whether 
or not the hook can be removed without causing further injury. All 
externally embedded hooks must be removed, unless hook removal would 
result in further injury to the turtle. No attempt should be made to 
remove a hook if it has been swallowed, or if it is determined that 
removal would result in further injury. If the hook cannot be 
removed and/or if the animal is entangled, as much line as possible 
must be removed prior to release, using a line cutter as specified 
in paragraph A.1. of this Appendix E. If the hook can be removed, it 
must be removed using a long-handled dehooker as specified in 
paragraphs A.2. and A.3. of this Appendix E. Without causing further 
injury, as much gear as possible must be removed from the turtle 
prior to its release. Refer to the careful release protocols and 
handling/release guidelines required in Sec.  622.10(c)(1), and the 
handling and resuscitation requirements specified in Sec.  
223.206(d)(1) for additional information.
    (b) [Reserved]

[FR Doc. 2011-33300 Filed 12-29-11; 8:45 am]
BILLING CODE 3510-22-P