Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic; Snapper-Grouper Fishery off the Southern Atlantic States; Amendment 14, 40824-40829 [E8-16252]
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Federal Register / Vol. 73, No. 137 / Wednesday, July 16, 2008 / Proposed Rules
approves a state rule implementing a
Federal standard.
In reviewing SIP submissions, EPA’s
role is to approve state choices,
provided that they meet the criteria of
the Clean Air Act. In this context, in the
absence of a prior existing requirement
for the State to use voluntary consensus
standards (VCS), EPA has no authority
to disapprove a SIP submission for
failure to use VCS. It would thus be
inconsistent with applicable law for
EPA, when it reviews a SIP submission,
to use VCS in place of a SIP submission
that otherwise satisfies the provisions of
the Clean Air Act. Redesignation is an
action that affects the status of a
geographical area and does not impose
any new requirements on sources. Thus,
the requirements of section 12(d) of the
National Technology Transfer and
Advancement Act of 1995 (15 U.S.C.
272 note) do not apply. As required by
section 3 of Executive Order 12988 (61
FR 4729, February 7, 1996), in issuing
this proposed rule, EPA has taken the
necessary steps to eliminate drafting
errors and ambiguity, minimize
potential litigation, and provide a clear
legal standard for affected conduct. EPA
has complied with Executive Order
12630 (53 FR 8859, March 15, 1988) by
examining the takings implications of
the rule in accordance with the
‘‘Attorney General’s Supplemental
Guidelines for the Evaluation of Risk
and Avoidance of Unanticipated
Takings’’ issued under the executive
order. This rule proposing to approve
the redesignation of the Tioga Area to
attainment for the 8-hour ozone
NAAQS, the associated maintenance
plan, the 2002 base year inventory, and
the MVEBs identified in the
maintenance plan, does not impose an
information collection burden under the
provisions of the Paperwork Reduction
Act of 1995 (44 U.S.C. 3501 et seq.).
This rule, proposing to approve the
redesignation of the Greene County Area
to attainment for the 8-hour ozone
NAAQS, the associated maintenance
plan, the 2002 base-year inventory, and
the MVEBs identified in the
maintenance plan, does not impose an
information collection burden under the
provisions of the Paperwork Reduction
Act of 1995 (44 U.S.C. 3501 et seq.).
List of Subjects
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40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Nitrogen oxides, Ozone,
Reporting and recordkeeping
requirements, Volatile organic
compounds.
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40 CFR Part 81
Air pollution control, National parks,
Wilderness areas.
Authority: 42 U.S.C. 7401 et seq.
Dated: July 3, 2008.
Donald S. Welsh,
Regional Administrator, Region III.
[FR Doc. E8–16278 Filed 7–15–08; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 622
[Docket No. 0612242911–7380–01]
RIN 0648–AU28
Fisheries of the Caribbean, Gulf of
Mexico, and South Atlantic; SnapperGrouper Fishery off the Southern
Atlantic States; Amendment 14
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule; request for
comments.
AGENCY:
SUMMARY: NMFS issues this proposed
rule to implement the applicable
provisions of Amendment 14 to the
Fishery Management Plan for the
Snapper-Grouper Fishery of the South
Atlantic Region (FMP), as prepared and
submitted by the South Atlantic Fishery
Management Council (Council).
Amendment 14 proposes, and this rule
would implement, establishment of
eight marine protected areas (MPAs) in
which fishing for or possession of South
Atlantic snapper-grouper would be
prohibited. The prohibition on
possession would not apply to a person
aboard a vessel that was in transit with
fishing gear appropriately stowed.
Amendment 14 also proposes to
prohibit the use of shark bottom
longlines within the MPAs, however,
NMFS is proposing to implement the
prohibition of shark bottom longlines
through separate rulemaking. The
intended effects of this proposed rule
are to protect a portion of the
population and habitat of long-lived,
slow growing, deepwater snappergrouper from fishing pressure to achieve
a more natural sex ratio, age, and size
structure within the proposed MPAs,
while minimizing adverse social and
economic effects.
DATES: Written comments on this
proposed rule must be received no later
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than 5 p.m., eastern time, on August 15,
2008.
ADDRESSES: You may submit comments,
identified by ‘‘0648–AU28’’, by any of
the following methods:
• Electronic Submissions: Submit all
electronic public comments via the
Federal e-Rulemaking Portal https://
www.regulations.gov.
• Fax: 727–824–5308; Attention: Kate
Michie.
• Mail: Kate Michie, Southeast
Regional Office, NMFS, 263 13th
Avenue South, St. Petersburg, FL 33701.
Instructions: All comments received
are a 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 publicly accessible. Do not
submit Confidential Business
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 file formats only.
Copies of Amendment 14 may be
obtained from the South Atlantic
Fishery Management Council, 4055
Faber Place, Suite 201, North
Charleston, SC 29405; phone: 843–571–
4366 or 866–SAFMC–10 (toll free); fax:
843–769–4520; e-mail:
safmc@safmc.net. Amendment 14
includes a Final Environmental Impact
Statement (FEIS), a Biological
Assessment, an Initial Regulatory
Flexibility Analysis (IRFA), a Regulatory
Impact Review, and a Social Impact
Assessment/Fishery Impact Statement.
FOR FURTHER INFORMATION CONTACT: Kate
Michie, telephone: 727–824–5305, fax:
727–824–5308, e-mail:
Kate.Michie@noaa.gov.
The
snapper-grouper fishery off the southern
Atlantic states is managed under the
FMP. The FMP was prepared by the
Council and is implemented under the
authority of the Magnuson-Stevens
Fishery Conservation and Management
Act (Magnuson-Stevens Act) by
regulations at 50 CFR part 622. NMFS
issues this proposed rule to implement
the applicable provisions of
Amendment 14 to the FMP. The
Atlantic shark fishery is managed under
the Consolidated Highly Migratory
Species Fishery Management Plan (HMS
FMP). The HMS FMP is implemented
under the authority of the MagnusonStevens Act by regulations at 50 CFR
part 635.
SUPPLEMENTARY INFORMATION:
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Background
Many snapper-grouper species are
vulnerable to overfishing because they
are long-lived (e.g., snowy grouper,
golden tilefish, red snapper, gag, scamp,
red grouper, and red porgy); they are
protogynous, i.e., they may change sex
from females to males as they grow
older/larger (e.g., snowy grouper,
speckled hind, Warsaw grouper,
yellowedge grouper, gag, scamp, red
porgy, and black sea bass); they form
spawning aggregations (e.g., snowy
grouper, gag, scamp, and red snapper);
and they suffer high release mortality
when taken from deep water. Deepwater
snapper-grouper species (speckled hind,
snowy grouper, Warsaw grouper,
yellowedge grouper, misty grouper,
golden tilefish, and blueline tilefish) are
most vulnerable to overfishing because
they live longer than 50 years, do not
survive the trauma of capture, and are
protogynous (groupers) or exhibit sexual
dimorphism, i.e., males and females
grow at different rates (tilefishes).
Stock assessments indicate that black
sea bass, red porgy, and snowy grouper
are overfished, i.e., spawning stock
biomass is not sufficient to reproduce
and support continued productivity. In
addition, black sea bass, golden tilefish,
snowy grouper, and vermilion snapper
are experiencing overfishing, i.e., the
current rate of fishing mortality
jeopardizes the capacity of the fishery to
produce its maximum sustainable yield
on a continuing basis. Reductions in
catch and protection of habitat are
needed.
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Proposed Measures
This rule would establish eight MPAs
in which a portion of the population
and habitat of long-lived, slow growing,
deepwater snapper-grouper species
would be protected from directed
fishing pressure. Fishing for or
possession of South Atlantic snappergrouper would be prohibited in the
MPAs. However, the prohibition on
possession would not apply to a person
aboard a vessel that was in transit with
fishing gear appropriately stowed, as
specified in § 622.35(i)(2) of this
proposed rule. MPAs are considered to
be the most effective fishery
management tool that would allow
deepwater snapper-grouper to reach a
more natural sex ratio, age, and size
structure, protect spawning locations,
and provide a refuge for early
developmental stages of fish species.
Using a collaborative process, the
Council selected specific sites for MPAs
on the basis of maximizing the
biological benefits and enhancing
enforceability and monitoring while
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minimizing the adverse social and
economic effects. Sizes of the MPAs
would range from approximately 5 by
10 nautical miles (nm) to approximately
22 by 23 nm. One would be off North
Carolina, three off South Carolina, one
off Georgia, and three off the east coast
of Florida. An artificial reef may be
established at one of the South Carolina
sites. The two most southern MPAs
would be approximately 9 and 13 nm
offshore, respectively, and the others at
least 38 nm offshore. The eight
proposed MPAs and their relative
locations are shown in Figure 1.
The prohibition of use of shark
bottom longlines in the MPAs is
considered necessary for habitat
protection and to prevent the mortality
of incidentally caught snapper-grouper.
The Council voted to include this
prohibition in Amendment 14 because
of concerns regarding the enforcement
of fishing activities by vessels that hold
permits in both the snapper-grouper and
shark bottom longline fisheries, both of
which deploy similar gear. However,
because the Atlantic shark fishery is
managed under the HMS FMP, NMFS
requested the HMS Division promulgate
the prohibition of use of shark bottom
longlines within the proposed MPAs.
The HMS Division published a final
rule on June 24, 2008 (72 FR 35778),
prohibiting shark bottom longlining in
the proposed MPAs through
Amendment 2 to the consolidated HMS
FMP.
Availability of Amendment 14
Additional background and rationale
for the measures discussed above are
contained in Amendment 14. The
availability of Amendment 14 was
announced in the Federal Register on
June 6, 2008, (73 FR 32281). Written
comments on Amendment 14 will be
accepted through August 5, 2008. All
comments received on Amendment 14
or on this proposed rule during their
respective comment periods will be
addressed in the preamble to the final
rule.
Classification
Pursuant to section 304(b)(1)(A) of the
Magnuson-Stevens Act, the NMFS
Assistant Administrator has determined
that this proposed rule is consistent
with Amendment 14, the MagnusonStevens Act, and other applicable law,
subject to further consideration after
public comment.
This proposed rule has been
determined to be not significant for
purposes of Executive Order 12866.
The Council prepared an FEIS for
Amendment 14; a notice of availability
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40825
was published on June 13, 2008 (73 FR
33813).
NMFS prepared an IRFA, as required
by section 603 of the Regulatory
Flexibility Act, for this proposed rule.
The IRFA describes the economic
impact this proposed rule, if adopted,
would have on small entities. A
description of the action, why it is being
considered, and the objectives of, and
legal basis for this action are contained
at the beginning of this section in the
preamble and in the SUMMARY section of
the preamble. A copy of the full analysis
is available from the Council (see
ADDRESSES). A summary of the IRFA
follows.
This proposed rule would establish
eight MPAs in the Federal waters of the
South Atlantic and prohibit fishing for
or possession of South Atlantic snappergrouper within any of the MPAs. The
purpose of this proposed rule is to assist
in the recovery of overfished stocks and
persistence of healthy fish stocks,
fisheries, and habitats. The MagnusonStevens Act provides the statutory basis
for the proposed rule.
No duplicative, overlapping, or
conflicting Federal rules have been
identified.
Two general classes of small business
entities would be directly affected by
the proposed rule, commercial fishing
vessels and for-hire fishing vessels. The
Small Business Administration defines
a small entity in the commercial fishing
sector as a firm that is independently
owned and operated, is not dominant in
its field of operation, and has average
annual gross receipts not in excess of $4
million (2002 NAICS 11411). For a forhire business, the appropriate revenue
benchmark is $6.5 million (2002 NAICS
487210).
Average net incomes estimated from
boats operating in the South Atlantic
snapper-grouper fishery were sampled
in a 1994 study that separated the
fishery into northern and southern
zones. The northern zone includes the
area north of 28° N. latitude to the North
Carolina/Virginia border. The southern
zone includes the area south of 25° N.
latitude to the border between the South
Atlantic and Gulf of Mexico Fishery
Management Councils. The estimated
average net incomes, in 1994 (and 2006)
dollars, were $83,224 ($113,212) for
boats that primarily used bottom
longlines in the northern zone, $23,075
($31,389) for boats that primarily used
black sea bass pots in the northern zone,
$15,563 ($21,171) for boats that
primarily used bottom longlines in the
southern zone, $11,649 ($15,842) for
boats that primarily used vertical lines
in the southern zone, and $8,307
($11,300) for boats that primarily used
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vertical lines in the northern zone.
Overall, boats in the northern zone
averaged $14,143 ($19,239) in net
income based on average revenues of
$48,702 ($66,250), while boats in the
southern zone averaged $12,388
($16,852) net income based on average
revenues of $39,745 ($54,066). More
recent data from the Southeast logbook
program show the average annual exvessel revenue from landings of
snapper-grouper species per vessel from
1999 to 2003 to range from $14,408 to
$16,376 (2006 dollars).
Although some fleet activity may exist
in this fishery, the extent of such has
not been determined. Thus, all vessels
are assumed to be unique business
entities. Given historic income data and
the gross revenue profile captured by
the Southeast logbook program, it is
determined that all vessels that would
be affected by the proposed rule are
small entities.
Charterboats are defined as boats for
hire carrying six or fewer passengers
that charge a fee to rent the entire boat.
Headboats tend to be larger, generally
can carry a maximum of around 60
passengers, and the fee is paid on an
individual angler basis. This analysis,
which estimates the range of the average
gross revenues in 2006 dollars for this
sector, is as follows: $61,714 to $83,820
for charterboats on the Atlantic coast of
Florida; $72,768 to $88,778 for
charterboats in North Carolina, $31,830
to $38,833 for charterboats in South
Carolina; $68,629 to $83,486 for
charterboats in Georgia; $170,276 to
$362,482 for headboats in Florida; and
$148,840 to $317,030 for headboats in
the other South Atlantic states. Similar
to the situation with the commercial
harvest sector, some fleet activity may
exist within the for-hire sector. The
magnitude and identity of such is
unknown, however, and all vessels are
assumed to represent unique business
entities. Given the gross revenue
profiles provided, vessels in the for-hire
recreational sector are determined to be
small business entities.
There were 1,066 commercial
snapper-grouper permitted vessels in
the South Atlantic during 2004. A
number of these permitted vessels were
not active in the snapper-grouper
fishery. It is not possible to estimate the
total number of true latent permits (i.e.,
those permits which are not expected to
be fished in any given year and may
exist only for speculative purposes)
since permits with no associated
landings could become active in a
subsequent year. The number of
permitted vessels, however, is an upper
bound on the universe of vessels in this
fishery. The assumed lower bound of
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the universe of vessels is the number of
active vessels in the latest year for
which data are available. This lower
bound estimate is 906 vessels, which is
the number of vessels/permits with
recorded landings of snapper-grouper
species in the South Atlantic in 2003.
The upper bound is the 1,066
commercial snapper-grouper permitted
vessels in the South Atlantic during
2004. Thus, the range of vessels
assumed to potentially operate in the
commercial snapper-grouper fishery is
906 to 1,066. Currently, there is
insufficient information to determine
the number of commercial fishing
vessels that fish for or possess any
snapper-grouper species in the proposed
MPAs.
In the for-hire sector, 1,594 snappergrouper for-hire permits were issued to
vessels in the South Atlantic states in
2004. The for-hire fishery operates as an
open access fishery, and not all of the
permitted snapper-grouper for-hire
vessels are necessarily active in this
fishery. Some vessel owners have been
known to purchase open access permits
as insurance for uncertainties in the
fisheries in which they currently
operate. Currently, there is insufficient
information to assess the number of forhire vessels that fish for or possess any
snapper-grouper species in the proposed
MPAs.
There is insufficient information to
assess the numbers or percentages of
commercial and for-hire vessels that fish
for or possess snapper-grouper species
in the proposed MPAs and would be
directly affected by the proposed rule.
Consequently, it cannot be determined
if the proposed rule would affect a
substantial number of small entities. A
direct cost of the proposed rule would
be the lost revenues and profits derived
from fishing for or possessing snappergrouper species in those areas. It is
expected that any vessel that
historically fished in these areas would
mitigate some of these losses by
relocating to other areas. There is
insufficient information to quantify any
potential losses of revenues and profits
from the creation of the MPAs.
However, the relatively small sizes of
the MPAs suggest there would not be
significant adverse economic impact.
Three alternatives, including the
status quo, were considered for the first
of the eight actions. Both the proposed
action (Alternative 1) and Alternative 2
would establish an MPA at the area of
the Snowy (Grouper) Wreck off the coast
of North Carolina. The proposed MPA is
55 nm southeast of Southport, North
Carolina, and Alternative 2 is located
approximately 57 nm southeast of
Southport. Each MPA is about 15 by 10
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nm. Fishermen from Little River,
Carolina Beach, and Southport ports
would most likely be affected by either
alternative. The proposed MPA and the
MPA specified by Alternative 2 include
an area ranging from 150 meters (m) to
300 m deep. The proposed MPA
includes a shallow area ranging from 60
to 100 m, while the MPA specified by
Alternative 2 includes a deeper area
exceeding 300 m in depth. Alternative
2 could result in the displacement of
fewer fishermen than the proposed
action, but would not be expected to
protect as many mid-shelf species as the
proposed action. The status quo
alternative (Alternative 3) would not
create an MPA in the Snowy (Grouper)
Wreck area off the coast of North
Carolina, would not increase the
protection of mid-shelf and deepwater
snapper-grouper species, and would
not, therefore, meet the Council’s
objective.
Four alternatives, including the status
quo, were considered for the second
action. The proposed action (Alternative
2) and two of the other alternatives
(Alternatives 1 and 3) would establish
an MPA off the northern South Carolina
coast. The proposed MPA is located
approximately 54 nm from Murrells
Inlet, while Alternative 1 is located
approximately 61 nm from Murrells
Inlet, and the MPA specified by
Alternative 3 is about 65 nm from
Murrells Inlet. The proposed MPA and
the MPAs specified by Alternatives 1
and 3 are 10 by 5 nm in size. Both the
proposed MPA and the MPA specified
by Alternative 1 run east to west, while
the MPA specified by Alternative 3 runs
parallel to shore. Waters in the proposed
MPA area range from 50 to 180 m deep.
The MPAs specified by Alternatives 1
and 3 share an area ranging in depth
from 70 to 140 m, but the MPA specified
by Alternative 1 includes more shallow
waters, while the MPA specified by
Alternative 3 includes a greater area of
deep water. The proposed MPA is
expected to protect more deepwater and
mid-shelf snapper-grouper species than
the MPAs specified by Alternatives 1
and 3. The status quo alternative
(Alternative 4) would not create an MPA
off the coast of northern South Carolina,
would not increase the protection of
mid-shelf and deepwater snappergrouper species, and would not,
therefore, meet the Council’s objective.
Three alternatives, including the
status quo, were considered for the third
action. Both the proposed action
(Alternative 1) and Alternative 2 would
establish an MPA off the coast of central
South Carolina. The proposed MPA is
oriented perpendicular to the coast and
is located about 45 nm southeast of
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Charleston Harbor. The MPA specified
by Alternative 2 is oriented parallel to
the shoreline and is located
approximately 50 nm southeast of
Charleston Harbor. Both MPAs are 10 by
5 nm in size. The proposed MPA is
expected to protect more mid-shelf and
rare deepwater snapper-grouper species
than Alternative 2. The status quo
alternative (Alternative 3) would not
create an MPA off the coast of central
South Carolina, would not increase the
protection of mid-shelf and deepwater
snapper-grouper species, and would
not, therefore, meet the Council’s
objective.
Three alternatives, including the
status quo, were considered for the
fourth action. Both the proposed action
(Alternative 1) and Alternative 2 would
establish an MPA off the coast of
Georgia. The proposed MPA is located
approximately 69 nm southeast of the
mouth of Wassaw Sound, while the
MPA specified by Alternative 2 is
located about 65 nm southeast of the
mouth of Wassaw Sound. Both the
proposed MPA and the MPA specified
by Alternative 2 are 10 by 10 nm in size,
and both share a common area with
waters 90 to 210 m deep. However, the
proposed MPA also includes waters
ranging from 90 to 300 m deep and runs
parallel to the shore, while the MPA
specified by Alternative 2 includes an
area with a wider depth range, from 65
to 380 m and does not run parallel to
the coast. The proposed MPA is
expected to be easier for industry to
maneuver around and may result in
greater protection of the mid-shelf
habitat that serves as a nursery for
deepwater species, notably tilefish, than
the MPA specified by Alternative 2. The
status quo alternative (Alternative 3)
would not create an MPA off the coast
of Georgia, would not increase the
protection of tilefish, snowy grouper,
and mid-shelf snapper-grouper species,
and would not, therefore, meet the
Council’s objective.
Seven alternatives, including the
status quo, were considered for the fifth
action. The proposed action (Alternative
4) and five of the other alternatives
would establish an MPA off the coast of
north Florida. The proposed MPA is
approximately 60 nm off the mouth of
St. John’s River near Jacksonville. The
MPA specified by Alternative 1 is
approximately 57 nm off the mouth of
the St. John’s River; the MPA specified
by Alternative 2 is about 47 nm east of
St. Augustine; the MPA specified by
Alternative 3 is approximately 43 nm off
New Smyrna Beach; the MPA specified
by Alternative 5 is about 55 nm east of
St. Augustine; and the MPA specified by
Alternative 6 is approximately 45 nm off
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New Smyrna Beach. The proposed MPA
and the MPAs specified by Alternatives
1, 2, and 5 are 10 by 10 nm in size,
while the MPAs specified by
Alternatives 3 and 6 are 22 by 23 nm in
size. The proposed MPA shares an area
with the MPA specified by Alternative
1 that ranges from 60 to 200 m in depth.
The proposed MPA also includes deeper
waters, ranging from 200 to 380 m in
depth, while the MPA specified by
Alternative 1 includes an area of
shallower water, ranging from 50 to 80
m in depth. The MPAs specified by
Alternatives 2 and 5 share an area with
depths ranging from 90 to 150 m. The
MPA specified by Alternative 5 also
includes a deeper area that ranges from
150 to 390 m, while the MPA specified
by Alternative 2 includes a shallower
area of 55 to 80 m. Most of the area
included by the MPAs specified by
Alternatives 3 and 6 overlap in an area
ranging from 200 to 690 m deep. The
MPA specified by Alternative 3 also
includes a deeper area that exceeds 700
m, while the MPA specified by
Alternative 6 includes a shallower area
of 80 to 150 m. Although the MPAs
specified by Alternatives 1 and 2 would
protect more mid-shelf snapper-grouper
species than the proposed MPA, while
the MPAs specified by Alternatives 3, 5
and 6 would protect more deepwater
species, these alternatives would also be
expected to result in greater adverse
economic impacts than the proposed
MPA. The status quo alternative
(Alternative 7), would not create an
MPA off the coast of north Florida,
would not increase the protection of
mid-shelf and deepwater snappergrouper species, and would not,
therefore, meet the Council’s objective.
Two alternatives, including the status
quo, were considered for the sixth
action. The proposed action would
establish an MPA in the area known as
Sea Bass Rocks off the coast of Florida.
The status quo alternative would not
create an MPA in this area, would not
increase the protection of deepwater
snapper-grouper species in this area,
and would not, therefore, meet the
Council’s objective.
Two alternatives, including the status
quo, were considered for the seventh
action. The proposed action would
establish an MPA in the vicinity of the
area known as East Hump and Unnamed
Hump off the coast of the Florida Keys.
The status quo alternative, would not
create an MPA in this area, would not
increase the protection of deepwater
snapper-grouper and protected species
in this area, and would not, therefore,
meet the Council’s objectives.
Two alternatives, including the status
quo, were considered for the eighth
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action. The proposed action would
establish an artificial reef MPA off the
coast of South Carolina. The status quo
alternative would not create this MPA,
would not increase the opportunity to
improve snapper-grouper populations in
this area, and would not, therefore, meet
the Council’s objective.
List of Subjects in 50 CFR Part 622
Fisheries, Fishing, Puerto Rico,
Reporting and recordkeeping
requirements, Virgin Islands.
Dated: July 10, 2008.
Samuel D. Rauch III,
Deputy Assistant Administrator For
Regulatory Programs, National Marine
Fisheries Service.
For the reasons set out in the
preamble, 50 CFR part 622 is proposed
to be amended as follows:
PART 622—FISHERIES OF THE
CARIBBEAN, GULF, AND SOUTH
ATLANTIC
1. The authority citation for part 622
continues to read as follows:
Authority: 16 U.S.C. 1801 et seq.
2. In § 622.2, the definition of ‘‘MPA’’
is added in alphabetical order to read as
follows:
§ 622.2
Definitions and acronyms.
*
*
*
*
*
MPA means marine protected area.
*
*
*
*
*
3. In § 622.35, paragraph (i) is added
to read as follows:
§ 622.35 Atlantic EEZ seasonal and/or area
closures.
*
*
*
*
*
(i) MPAs. (1) No person may fish for
a South Atlantic snapper-grouper in an
MPA, and no person may possess a
South Atlantic snapper-grouper in an
MPA. However, the prohibition on
possession does not apply to a person
aboard a vessel that is in transit with
fishing gear appropriately stowed as
specified in paragraph (i)(2) of this
section. In addition to these restrictions,
see § 635.21(d)(1)(iii) of this chapter
regarding restrictions applicable within
these MPAs for any vessel issued a
permit under part 635 of this chapter
that has longline gear on board. MPAs
consist of deepwater areas as follows:
(i) Snowy Grouper Wreck MPA is
bounded by rhumb lines connecting, in
order, the following points:
Point
A
B
C
D
A
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North lat.
33°25′
33°34.75′
33°25.5′
33°15.75′
33°25′
16JYP1
West long.
77°04.75′
76°51.3′
76°46.5′
77°00.0′
77°04.75′
40828
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(ii) Northern South Carolina MPA is
bounded on the north by 32°53.5′ N.
lat.; on the south by 32°48.5′ N. lat.; on
the east by 78°04.75′ W. long.; and on
the west by 78°16.75′ W. long.
(iii) Edisto MPA is bounded on the
north by 32°24′ N. lat.; on the south by
32°18.5′ N. lat.; on the east by 78°54.0′
W. long.; and on the west by 79°06.0′ W.
long.
(iv) Charleston Deep Artificial Reef
MPA is bounded by rhumb lines
connecting, in order, the following
points:
Point
A
B
C
D
A
North lat.
32°04′
32°08.5′
32°06′
32°01.5′
32°04′
West long.
79°12′
79°07.5′
79°05′
79°09.3′
79°12′
jlentini on PROD1PC65 with PROPOSALS
A
B
C
VerDate Aug<31>2005
North lat.
31°43′
31°43′
31°34′
17:14 Jul 15, 2008
West long.
79°31′
79°21′
79°29′
Jkt 214001
D
A
North lat.
31°34′
31°43′
West long.
79°39′
79°31′
(vi) North Florida MPA is bounded on
the north by 30°29′ N. lat.; on the south
by 30°19′ N. lat.; on the east by 80°02′
W. long.; and on the west by 80°14′ W.
long.
(vii) St. Lucie Hump MPA is bounded
on the north by 27°08′ N. lat.; on the
south by 27°04′ N. lat.; on the east by
79°58′ W. long.; and on the west by
80°00′ W. long.
(viii) East Hump MPA is bounded by
rhumb lines connecting, in order, the
following points:
Point
(v) Georgia MPA is bounded by rhumb
lines connecting, in order, the following
points:
Point
Point
A
B
C
D
A
North lat.
24°36.5′
24°32′
24°27.5′
24°32.5′
24°36.5′
West long.
80°45.5′
80°36′
80°38.5′
80°48′
80°45.5′
(2) For the purpose of paragraph (i)(1)
of this section, transit means direct,
non-stop progression through the MPA.
Fishing gear appropriately stowed
means—
PO 00000
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Fmt 4702
Sfmt 4702
(i) A longline may be left on the drum
if all gangions and hooks are
disconnected and stowed below deck.
Hooks cannot be baited. All buoys must
be disconnected from the gear; however,
buoys may remain on deck.
(ii) A trawl or try net may remain on
deck, but trawl doors must be
disconnected from such net and must be
secured.
(iii) A gillnet, stab net, or trammel net
must be left on the drum. Any
additional such nets not attached to the
drum must be stowed below deck.
(iv) Terminal gear (i.e., hook, leader,
sinker, flasher, or bait) used with an
automatic reel, bandit gear, buoy gear,
handline, or rod and reel must be
disconnected and stowed separately
from such fishing gear. A rod and reel
must be removed from the rod holder
and stowed securely on or below deck.
(v) A crustacean trap, golden crab
trap, or sea bass pot cannot be baited.
All buoys must be disconnected from
the gear; however, buoys may remain on
deck.
4. Add Figure 1 to Part 622 to read as
follows:
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16JYP1
Federal Register / Vol. 73, No. 137 / Wednesday, July 16, 2008 / Proposed Rules
40829
[FR Doc. E8–16252 Filed 7–15–08; 8:45 am]
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17:14 Jul 15, 2008
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E:\FR\FM\16JYP1.SGM
16JYP1
EP16JY08.009
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BILLING CODE 3510–22–S
Agencies
[Federal Register Volume 73, Number 137 (Wednesday, July 16, 2008)]
[Proposed Rules]
[Pages 40824-40829]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-16252]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 622
[Docket No. 0612242911-7380-01]
RIN 0648-AU28
Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic;
Snapper-Grouper Fishery off the Southern Atlantic States; Amendment 14
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Proposed rule; request for comments.
-----------------------------------------------------------------------
SUMMARY: NMFS issues this proposed rule to implement the applicable
provisions of Amendment 14 to the Fishery Management Plan for the
Snapper-Grouper Fishery of the South Atlantic Region (FMP), as prepared
and submitted by the South Atlantic Fishery Management Council
(Council). Amendment 14 proposes, and this rule would implement,
establishment of eight marine protected areas (MPAs) in which fishing
for or possession of South Atlantic snapper-grouper would be
prohibited. The prohibition on possession would not apply to a person
aboard a vessel that was in transit with fishing gear appropriately
stowed. Amendment 14 also proposes to prohibit the use of shark bottom
longlines within the MPAs, however, NMFS is proposing to implement the
prohibition of shark bottom longlines through separate rulemaking. The
intended effects of this proposed rule are to protect a portion of the
population and habitat of long-lived, slow growing, deepwater snapper-
grouper from fishing pressure to achieve a more natural sex ratio, age,
and size structure within the proposed MPAs, while minimizing adverse
social and economic effects.
DATES: Written comments on this proposed rule must be received no later
than 5 p.m., eastern time, on August 15, 2008.
ADDRESSES: You may submit comments, identified by ``0648-AU28'', by any
of the following methods:
Electronic Submissions: Submit all electronic public
comments via the Federal e-Rulemaking Portal https://
www.regulations.gov.
Fax: 727-824-5308; Attention: Kate Michie.
Mail: Kate Michie, Southeast Regional Office, NMFS, 263
13\th\ Avenue South, St. Petersburg, FL 33701.
Instructions: All comments received are a 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 publicly
accessible. Do not submit Confidential Business 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 file formats only.
Copies of Amendment 14 may be obtained from the South Atlantic
Fishery Management Council, 4055 Faber Place, Suite 201, North
Charleston, SC 29405; phone: 843-571-4366 or 866-SAFMC-10 (toll free);
fax: 843-769-4520; e-mail: safmc@safmc.net. Amendment 14 includes a
Final Environmental Impact Statement (FEIS), a Biological Assessment,
an Initial Regulatory Flexibility Analysis (IRFA), a Regulatory Impact
Review, and a Social Impact Assessment/Fishery Impact Statement.
FOR FURTHER INFORMATION CONTACT: Kate Michie, telephone: 727-824-5305,
fax: 727-824-5308, e-mail: Kate.Michie@noaa.gov.
SUPPLEMENTARY INFORMATION: The snapper-grouper fishery off the southern
Atlantic states is managed under the FMP. The FMP was prepared by the
Council and is implemented under the authority of the Magnuson-Stevens
Fishery Conservation and Management Act (Magnuson-Stevens Act) by
regulations at 50 CFR part 622. NMFS issues this proposed rule to
implement the applicable provisions of Amendment 14 to the FMP. The
Atlantic shark fishery is managed under the Consolidated Highly
Migratory Species Fishery Management Plan (HMS FMP). The HMS FMP is
implemented under the authority of the Magnuson-Stevens Act by
regulations at 50 CFR part 635.
[[Page 40825]]
Background
Many snapper-grouper species are vulnerable to overfishing because
they are long-lived (e.g., snowy grouper, golden tilefish, red snapper,
gag, scamp, red grouper, and red porgy); they are protogynous, i.e.,
they may change sex from females to males as they grow older/larger
(e.g., snowy grouper, speckled hind, Warsaw grouper, yellowedge
grouper, gag, scamp, red porgy, and black sea bass); they form spawning
aggregations (e.g., snowy grouper, gag, scamp, and red snapper); and
they suffer high release mortality when taken from deep water.
Deepwater snapper-grouper species (speckled hind, snowy grouper, Warsaw
grouper, yellowedge grouper, misty grouper, golden tilefish, and
blueline tilefish) are most vulnerable to overfishing because they live
longer than 50 years, do not survive the trauma of capture, and are
protogynous (groupers) or exhibit sexual dimorphism, i.e., males and
females grow at different rates (tilefishes).
Stock assessments indicate that black sea bass, red porgy, and
snowy grouper are overfished, i.e., spawning stock biomass is not
sufficient to reproduce and support continued productivity. In
addition, black sea bass, golden tilefish, snowy grouper, and vermilion
snapper are experiencing overfishing, i.e., the current rate of fishing
mortality jeopardizes the capacity of the fishery to produce its
maximum sustainable yield on a continuing basis. Reductions in catch
and protection of habitat are needed.
Proposed Measures
This rule would establish eight MPAs in which a portion of the
population and habitat of long-lived, slow growing, deepwater snapper-
grouper species would be protected from directed fishing pressure.
Fishing for or possession of South Atlantic snapper-grouper would be
prohibited in the MPAs. However, the prohibition on possession would
not apply to a person aboard a vessel that was in transit with fishing
gear appropriately stowed, as specified in Sec. 622.35(i)(2) of this
proposed rule. MPAs are considered to be the most effective fishery
management tool that would allow deepwater snapper-grouper to reach a
more natural sex ratio, age, and size structure, protect spawning
locations, and provide a refuge for early developmental stages of fish
species.
Using a collaborative process, the Council selected specific sites
for MPAs on the basis of maximizing the biological benefits and
enhancing enforceability and monitoring while minimizing the adverse
social and economic effects. Sizes of the MPAs would range from
approximately 5 by 10 nautical miles (nm) to approximately 22 by 23 nm.
One would be off North Carolina, three off South Carolina, one off
Georgia, and three off the east coast of Florida. An artificial reef
may be established at one of the South Carolina sites. The two most
southern MPAs would be approximately 9 and 13 nm offshore,
respectively, and the others at least 38 nm offshore. The eight
proposed MPAs and their relative locations are shown in Figure 1.
The prohibition of use of shark bottom longlines in the MPAs is
considered necessary for habitat protection and to prevent the
mortality of incidentally caught snapper-grouper. The Council voted to
include this prohibition in Amendment 14 because of concerns regarding
the enforcement of fishing activities by vessels that hold permits in
both the snapper-grouper and shark bottom longline fisheries, both of
which deploy similar gear. However, because the Atlantic shark fishery
is managed under the HMS FMP, NMFS requested the HMS Division
promulgate the prohibition of use of shark bottom longlines within the
proposed MPAs. The HMS Division published a final rule on June 24, 2008
(72 FR 35778), prohibiting shark bottom longlining in the proposed MPAs
through Amendment 2 to the consolidated HMS FMP.
Availability of Amendment 14
Additional background and rationale for the measures discussed
above are contained in Amendment 14. The availability of Amendment 14
was announced in the Federal Register on June 6, 2008, (73 FR 32281).
Written comments on Amendment 14 will be accepted through August 5,
2008. All comments received on Amendment 14 or on this proposed rule
during their respective comment periods will be addressed in the
preamble to the final rule.
Classification
Pursuant to section 304(b)(1)(A) of the Magnuson-Stevens Act, the
NMFS Assistant Administrator has determined that this proposed rule is
consistent with Amendment 14, the Magnuson-Stevens Act, and other
applicable law, subject to further consideration after public comment.
This proposed rule has been determined to be not significant for
purposes of Executive Order 12866.
The Council prepared an FEIS for Amendment 14; a notice of
availability was published on June 13, 2008 (73 FR 33813).
NMFS prepared an IRFA, as required by section 603 of the Regulatory
Flexibility Act, for this proposed rule. The IRFA describes the
economic impact this proposed rule, if adopted, would have on small
entities. A description of the action, why it is being considered, and
the objectives of, and legal basis for this action are contained at the
beginning of this section in the preamble and in the SUMMARY section of
the preamble. A copy of the full analysis is available from the Council
(see ADDRESSES). A summary of the IRFA follows.
This proposed rule would establish eight MPAs in the Federal waters
of the South Atlantic and prohibit fishing for or possession of South
Atlantic snapper-grouper within any of the MPAs. The purpose of this
proposed rule is to assist in the recovery of overfished stocks and
persistence of healthy fish stocks, fisheries, and habitats. The
Magnuson-Stevens Act provides the statutory basis for the proposed
rule.
No duplicative, overlapping, or conflicting Federal rules have been
identified.
Two general classes of small business entities would be directly
affected by the proposed rule, commercial fishing vessels and for-hire
fishing vessels. The Small Business Administration defines a small
entity in the commercial fishing sector as a firm that is independently
owned and operated, is not dominant in its field of operation, and has
average annual gross receipts not in excess of $4 million (2002 NAICS
11411). For a for-hire business, the appropriate revenue benchmark is
$6.5 million (2002 NAICS 487210).
Average net incomes estimated from boats operating in the South
Atlantic snapper-grouper fishery were sampled in a 1994 study that
separated the fishery into northern and southern zones. The northern
zone includes the area north of 28[deg] N. latitude to the North
Carolina/Virginia border. The southern zone includes the area south of
25[deg] N. latitude to the border between the South Atlantic and Gulf
of Mexico Fishery Management Councils. The estimated average net
incomes, in 1994 (and 2006) dollars, were $83,224 ($113,212) for boats
that primarily used bottom longlines in the northern zone, $23,075
($31,389) for boats that primarily used black sea bass pots in the
northern zone, $15,563 ($21,171) for boats that primarily used bottom
longlines in the southern zone, $11,649 ($15,842) for boats that
primarily used vertical lines in the southern zone, and $8,307
($11,300) for boats that primarily used
[[Page 40826]]
vertical lines in the northern zone. Overall, boats in the northern
zone averaged $14,143 ($19,239) in net income based on average revenues
of $48,702 ($66,250), while boats in the southern zone averaged $12,388
($16,852) net income based on average revenues of $39,745 ($54,066).
More recent data from the Southeast logbook program show the average
annual ex-vessel revenue from landings of snapper-grouper species per
vessel from 1999 to 2003 to range from $14,408 to $16,376 (2006
dollars).
Although some fleet activity may exist in this fishery, the extent
of such has not been determined. Thus, all vessels are assumed to be
unique business entities. Given historic income data and the gross
revenue profile captured by the Southeast logbook program, it is
determined that all vessels that would be affected by the proposed rule
are small entities.
Charterboats are defined as boats for hire carrying six or fewer
passengers that charge a fee to rent the entire boat. Headboats tend to
be larger, generally can carry a maximum of around 60 passengers, and
the fee is paid on an individual angler basis. This analysis, which
estimates the range of the average gross revenues in 2006 dollars for
this sector, is as follows: $61,714 to $83,820 for charterboats on the
Atlantic coast of Florida; $72,768 to $88,778 for charterboats in North
Carolina, $31,830 to $38,833 for charterboats in South Carolina;
$68,629 to $83,486 for charterboats in Georgia; $170,276 to $362,482
for headboats in Florida; and $148,840 to $317,030 for headboats in the
other South Atlantic states. Similar to the situation with the
commercial harvest sector, some fleet activity may exist within the
for-hire sector. The magnitude and identity of such is unknown,
however, and all vessels are assumed to represent unique business
entities. Given the gross revenue profiles provided, vessels in the
for-hire recreational sector are determined to be small business
entities.
There were 1,066 commercial snapper-grouper permitted vessels in
the South Atlantic during 2004. A number of these permitted vessels
were not active in the snapper-grouper fishery. It is not possible to
estimate the total number of true latent permits (i.e., those permits
which are not expected to be fished in any given year and may exist
only for speculative purposes) since permits with no associated
landings could become active in a subsequent year. The number of
permitted vessels, however, is an upper bound on the universe of
vessels in this fishery. The assumed lower bound of the universe of
vessels is the number of active vessels in the latest year for which
data are available. This lower bound estimate is 906 vessels, which is
the number of vessels/permits with recorded landings of snapper-grouper
species in the South Atlantic in 2003. The upper bound is the 1,066
commercial snapper-grouper permitted vessels in the South Atlantic
during 2004. Thus, the range of vessels assumed to potentially operate
in the commercial snapper-grouper fishery is 906 to 1,066. Currently,
there is insufficient information to determine the number of commercial
fishing vessels that fish for or possess any snapper-grouper species in
the proposed MPAs.
In the for-hire sector, 1,594 snapper-grouper for-hire permits were
issued to vessels in the South Atlantic states in 2004. The for-hire
fishery operates as an open access fishery, and not all of the
permitted snapper-grouper for-hire vessels are necessarily active in
this fishery. Some vessel owners have been known to purchase open
access permits as insurance for uncertainties in the fisheries in which
they currently operate. Currently, there is insufficient information to
assess the number of for-hire vessels that fish for or possess any
snapper-grouper species in the proposed MPAs.
There is insufficient information to assess the numbers or
percentages of commercial and for-hire vessels that fish for or possess
snapper-grouper species in the proposed MPAs and would be directly
affected by the proposed rule. Consequently, it cannot be determined if
the proposed rule would affect a substantial number of small entities.
A direct cost of the proposed rule would be the lost revenues and
profits derived from fishing for or possessing snapper-grouper species
in those areas. It is expected that any vessel that historically fished
in these areas would mitigate some of these losses by relocating to
other areas. There is insufficient information to quantify any
potential losses of revenues and profits from the creation of the MPAs.
However, the relatively small sizes of the MPAs suggest there would not
be significant adverse economic impact.
Three alternatives, including the status quo, were considered for
the first of the eight actions. Both the proposed action (Alternative
1) and Alternative 2 would establish an MPA at the area of the Snowy
(Grouper) Wreck off the coast of North Carolina. The proposed MPA is 55
nm southeast of Southport, North Carolina, and Alternative 2 is located
approximately 57 nm southeast of Southport. Each MPA is about 15 by 10
nm. Fishermen from Little River, Carolina Beach, and Southport ports
would most likely be affected by either alternative. The proposed MPA
and the MPA specified by Alternative 2 include an area ranging from 150
meters (m) to 300 m deep. The proposed MPA includes a shallow area
ranging from 60 to 100 m, while the MPA specified by Alternative 2
includes a deeper area exceeding 300 m in depth. Alternative 2 could
result in the displacement of fewer fishermen than the proposed action,
but would not be expected to protect as many mid-shelf species as the
proposed action. The status quo alternative (Alternative 3) would not
create an MPA in the Snowy (Grouper) Wreck area off the coast of North
Carolina, would not increase the protection of mid-shelf and deepwater
snapper-grouper species, and would not, therefore, meet the Council's
objective.
Four alternatives, including the status quo, were considered for
the second action. The proposed action (Alternative 2) and two of the
other alternatives (Alternatives 1 and 3) would establish an MPA off
the northern South Carolina coast. The proposed MPA is located
approximately 54 nm from Murrells Inlet, while Alternative 1 is located
approximately 61 nm from Murrells Inlet, and the MPA specified by
Alternative 3 is about 65 nm from Murrells Inlet. The proposed MPA and
the MPAs specified by Alternatives 1 and 3 are 10 by 5 nm in size. Both
the proposed MPA and the MPA specified by Alternative 1 run east to
west, while the MPA specified by Alternative 3 runs parallel to shore.
Waters in the proposed MPA area range from 50 to 180 m deep. The MPAs
specified by Alternatives 1 and 3 share an area ranging in depth from
70 to 140 m, but the MPA specified by Alternative 1 includes more
shallow waters, while the MPA specified by Alternative 3 includes a
greater area of deep water. The proposed MPA is expected to protect
more deepwater and mid-shelf snapper-grouper species than the MPAs
specified by Alternatives 1 and 3. The status quo alternative
(Alternative 4) would not create an MPA off the coast of northern South
Carolina, would not increase the protection of mid-shelf and deepwater
snapper-grouper species, and would not, therefore, meet the Council's
objective.
Three alternatives, including the status quo, were considered for
the third action. Both the proposed action (Alternative 1) and
Alternative 2 would establish an MPA off the coast of central South
Carolina. The proposed MPA is oriented perpendicular to the coast and
is located about 45 nm southeast of
[[Page 40827]]
Charleston Harbor. The MPA specified by Alternative 2 is oriented
parallel to the shoreline and is located approximately 50 nm southeast
of Charleston Harbor. Both MPAs are 10 by 5 nm in size. The proposed
MPA is expected to protect more mid-shelf and rare deepwater snapper-
grouper species than Alternative 2. The status quo alternative
(Alternative 3) would not create an MPA off the coast of central South
Carolina, would not increase the protection of mid-shelf and deepwater
snapper-grouper species, and would not, therefore, meet the Council's
objective.
Three alternatives, including the status quo, were considered for
the fourth action. Both the proposed action (Alternative 1) and
Alternative 2 would establish an MPA off the coast of Georgia. The
proposed MPA is located approximately 69 nm southeast of the mouth of
Wassaw Sound, while the MPA specified by Alternative 2 is located about
65 nm southeast of the mouth of Wassaw Sound. Both the proposed MPA and
the MPA specified by Alternative 2 are 10 by 10 nm in size, and both
share a common area with waters 90 to 210 m deep. However, the proposed
MPA also includes waters ranging from 90 to 300 m deep and runs
parallel to the shore, while the MPA specified by Alternative 2
includes an area with a wider depth range, from 65 to 380 m and does
not run parallel to the coast. The proposed MPA is expected to be
easier for industry to maneuver around and may result in greater
protection of the mid-shelf habitat that serves as a nursery for
deepwater species, notably tilefish, than the MPA specified by
Alternative 2. The status quo alternative (Alternative 3) would not
create an MPA off the coast of Georgia, would not increase the
protection of tilefish, snowy grouper, and mid-shelf snapper-grouper
species, and would not, therefore, meet the Council's objective.
Seven alternatives, including the status quo, were considered for
the fifth action. The proposed action (Alternative 4) and five of the
other alternatives would establish an MPA off the coast of north
Florida. The proposed MPA is approximately 60 nm off the mouth of St.
John's River near Jacksonville. The MPA specified by Alternative 1 is
approximately 57 nm off the mouth of the St. John's River; the MPA
specified by Alternative 2 is about 47 nm east of St. Augustine; the
MPA specified by Alternative 3 is approximately 43 nm off New Smyrna
Beach; the MPA specified by Alternative 5 is about 55 nm east of St.
Augustine; and the MPA specified by Alternative 6 is approximately 45
nm off New Smyrna Beach. The proposed MPA and the MPAs specified by
Alternatives 1, 2, and 5 are 10 by 10 nm in size, while the MPAs
specified by Alternatives 3 and 6 are 22 by 23 nm in size. The proposed
MPA shares an area with the MPA specified by Alternative 1 that ranges
from 60 to 200 m in depth. The proposed MPA also includes deeper
waters, ranging from 200 to 380 m in depth, while the MPA specified by
Alternative 1 includes an area of shallower water, ranging from 50 to
80 m in depth. The MPAs specified by Alternatives 2 and 5 share an area
with depths ranging from 90 to 150 m. The MPA specified by Alternative
5 also includes a deeper area that ranges from 150 to 390 m, while the
MPA specified by Alternative 2 includes a shallower area of 55 to 80 m.
Most of the area included by the MPAs specified by Alternatives 3 and 6
overlap in an area ranging from 200 to 690 m deep. The MPA specified by
Alternative 3 also includes a deeper area that exceeds 700 m, while the
MPA specified by Alternative 6 includes a shallower area of 80 to 150
m. Although the MPAs specified by Alternatives 1 and 2 would protect
more mid-shelf snapper-grouper species than the proposed MPA, while the
MPAs specified by Alternatives 3, 5 and 6 would protect more deepwater
species, these alternatives would also be expected to result in greater
adverse economic impacts than the proposed MPA. The status quo
alternative (Alternative 7), would not create an MPA off the coast of
north Florida, would not increase the protection of mid-shelf and
deepwater snapper-grouper species, and would not, therefore, meet the
Council's objective.
Two alternatives, including the status quo, were considered for the
sixth action. The proposed action would establish an MPA in the area
known as Sea Bass Rocks off the coast of Florida. The status quo
alternative would not create an MPA in this area, would not increase
the protection of deepwater snapper-grouper species in this area, and
would not, therefore, meet the Council's objective.
Two alternatives, including the status quo, were considered for the
seventh action. The proposed action would establish an MPA in the
vicinity of the area known as East Hump and Unnamed Hump off the coast
of the Florida Keys. The status quo alternative, would not create an
MPA in this area, would not increase the protection of deepwater
snapper-grouper and protected species in this area, and would not,
therefore, meet the Council's objectives.
Two alternatives, including the status quo, were considered for the
eighth action. The proposed action would establish an artificial reef
MPA off the coast of South Carolina. The status quo alternative would
not create this MPA, would not increase the opportunity to improve
snapper-grouper populations in this area, and would not, therefore,
meet the Council's objective.
List of Subjects in 50 CFR Part 622
Fisheries, Fishing, Puerto Rico, Reporting and recordkeeping
requirements, Virgin Islands.
Dated: July 10, 2008.
Samuel D. Rauch III,
Deputy Assistant Administrator For Regulatory Programs, National Marine
Fisheries Service.
For the reasons set out in the preamble, 50 CFR part 622 is
proposed to be amended as follows:
PART 622--FISHERIES OF THE CARIBBEAN, GULF, AND SOUTH ATLANTIC
1. The authority citation for part 622 continues to read as
follows:
Authority: 16 U.S.C. 1801 et seq.
2. In Sec. 622.2, the definition of ``MPA'' is added in
alphabetical order to read as follows:
Sec. 622.2 Definitions and acronyms.
* * * * *
MPA means marine protected area.
* * * * *
3. In Sec. 622.35, paragraph (i) is added to read as follows:
Sec. 622.35 Atlantic EEZ seasonal and/or area closures.
* * * * *
(i) MPAs. (1) No person may fish for a South Atlantic snapper-
grouper in an MPA, and no person may possess a South Atlantic snapper-
grouper in an MPA. However, the prohibition on possession does not
apply to a person aboard a vessel that is in transit with fishing gear
appropriately stowed as specified in paragraph (i)(2) of this section.
In addition to these restrictions, see Sec. 635.21(d)(1)(iii) of this
chapter regarding restrictions applicable within these MPAs for any
vessel issued a permit under part 635 of this chapter that has longline
gear on board. MPAs consist of deepwater areas as follows:
(i) Snowy Grouper Wreck MPA is bounded by rhumb lines connecting,
in order, the following points:
------------------------------------------------------------------------
Point North lat. West long.
------------------------------------------------------------------------
A 33[deg]25' 77[deg]04.75'
B 33[deg]34.75' 76[deg]51.3'
C 33[deg]25.5' 76[deg]46.5'
D 33[deg]15.75' 77[deg]00.0'
A 33[deg]25' 77[deg]04.75'
------------------------------------------------------------------------
[[Page 40828]]
(ii) Northern South Carolina MPA is bounded on the north by
32[deg]53.5' N. lat.; on the south by 32[deg]48.5' N. lat.; on the east
by 78[deg]04.75' W. long.; and on the west by 78[deg]16.75' W. long.
(iii) Edisto MPA is bounded on the north by 32[deg]24' N. lat.; on
the south by 32[deg]18.5' N. lat.; on the east by 78[deg]54.0' W.
long.; and on the west by 79[deg]06.0' W. long.
(iv) Charleston Deep Artificial Reef MPA is bounded by rhumb lines
connecting, in order, the following points:
------------------------------------------------------------------------
Point North lat. West long.
------------------------------------------------------------------------
A 32[deg]04' 79[deg]12'
B 32[deg]08.5' 79[deg]07.5'
C 32[deg]06' 79[deg]05'
D 32[deg]01.5' 79[deg]09.3'
A 32[deg]04' 79[deg]12'
------------------------------------------------------------------------
(v) Georgia MPA is bounded by rhumb lines connecting, in order, the
following points:
------------------------------------------------------------------------
Point North lat. West long.
------------------------------------------------------------------------
A 31[deg]43' 79[deg]31'
B 31[deg]43' 79[deg]21'
C 31[deg]34' 79[deg]29'
D 31[deg]34' 79[deg]39'
A 31[deg]43' 79[deg]31'
------------------------------------------------------------------------
(vi) North Florida MPA is bounded on the north by 30[deg]29' N.
lat.; on the south by 30[deg]19' N. lat.; on the east by 80[deg]02' W.
long.; and on the west by 80[deg]14' W. long.
(vii) St. Lucie Hump MPA is bounded on the north by 27[deg]08' N.
lat.; on the south by 27[deg]04' N. lat.; on the east by 79[deg]58' W.
long.; and on the west by 80[deg]00' W. long.
(viii) East Hump MPA is bounded by rhumb lines connecting, in
order, the following points:
------------------------------------------------------------------------
Point North lat. West long.
------------------------------------------------------------------------
A 24[deg]36.5' 80[deg]45.5'
B 24[deg]32' 80[deg]36'
C 24[deg]27.5' 80[deg]38.5'
D 24[deg]32.5' 80[deg]48'
A 24[deg]36.5' 80[deg]45.5'
------------------------------------------------------------------------
(2) For the purpose of paragraph (i)(1) of this section, transit
means direct, non-stop progression through the MPA. Fishing gear
appropriately stowed means--
(i) A longline may be left on the drum if all gangions and hooks
are disconnected and stowed below deck. Hooks cannot be baited. All
buoys must be disconnected from the gear; however, buoys may remain on
deck.
(ii) A trawl or try net may remain on deck, but trawl doors must be
disconnected from such net and must be secured.
(iii) A gillnet, stab net, or trammel net must be left on the drum.
Any additional such nets not attached to the drum must be stowed below
deck.
(iv) Terminal gear (i.e., hook, leader, sinker, flasher, or bait)
used with an automatic reel, bandit gear, buoy gear, handline, or rod
and reel must be disconnected and stowed separately from such fishing
gear. A rod and reel must be removed from the rod holder and stowed
securely on or below deck.
(v) A crustacean trap, golden crab trap, or sea bass pot cannot be
baited. All buoys must be disconnected from the gear; however, buoys
may remain on deck.
4. Add Figure 1 to Part 622 to read as follows:
[[Page 40829]]
[GRAPHIC] [TIFF OMITTED] TP16JY08.009
[FR Doc. E8-16252 Filed 7-15-08; 8:45 am]
BILLING CODE 3510-22-S