Caribbean Fishery Management Council; Scoping Meetings, 2665-2672 [2011-712]
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Federal Register / Vol. 76, No. 10 / Friday, January 14, 2011 / Notices
form, legible copies of documents
supporting historical participation in
the American Samoa pelagic longline
fishery, and payment for the nonrefundable application processing fee,
in accordance with the regulations at 50
CFR 665.13. Applications must be
received by NMFS (see ADDRESSES) by
May 16, 2011 to be considered for a
permit; applications will not be
accepted if received after that date.
Authoritative additional information on
the American Samoa limited entry
program may be found in 50 CFR part
665.
Authority: 16 U.S.C. 1801 et seq.
Dated: January 10, 2011.
Emily H. Menashes,
Acting Director, Office of Sustainable
Fisheries, National Marine Fisheries Service.
[FR Doc. 2011–797 Filed 1–13–11; 8:45 am]
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DEPARTMENT OF COMMERCE
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[RIN 0648–XA107]
New England Fishery Management
Council; Public Meeting; Cancellation
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
AGENCY:
Notice of cancellation of a
public meeting.
ACTION:
The New England Fishery
Management Council has cancelled the
public meeting of its Herring Oversight
Committee that was scheduled for
Thursday, January 20, 2011.
SUMMARY:
Paul
J. Howard, Executive Director, New
England Fishery Management Council;
telephone: (978) 465–0492.
FOR FURTHER INFORMATION CONTACT:
The initial
notice was published on December 29,
2010, (75 FR 81972) and the meeting
will be rescheduled at a later date and
announced in the Federal Register.
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SUPPLEMENTARY INFORMATION:
Dated: January 10, 2011.
Tracey L. Thompson,
Acting Director, Office of Sustainable
Fisheries, National Marine Fisheries Service.
[FR Doc. 2011–688 Filed 1–13–11; 8:45 am]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XA146
Caribbean Fishery Management
Council; Scoping Meetings
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice of Scoping Meetings.
AGENCY:
The Caribbean Fishery
Management Council will hold scoping
meetings to obtain input from fishers,
the general public, and the local
agencies representatives on the Options
Paper for the Comprehensive Annual
Catch Limit (ACL) Amendment for the
U.S. Caribbean including Amendment 6
to the Reef Fish Fishery Management
Plan of Puerto Rico and the U.S. Virgin
Islands; Amendment 2 to the Fishery
Management Plan for Corals and Reef
Associated Plants and Invertebrates of
Puerto Rico and the U.S. Virgin Islands;
Amendment 5 to the Fishery
Management Plan for the Spiny Lobster
Fishery of Puerto Rico and the U.S.
Virgin Islands; Amendment 3 to the
Fishery Management Plan for the Queen
Conch Fishery of Puerto Rico and the
U.S. Virgin Islands
DATES AND ADDRESSES: The scoping
meetings will be held on the following
dates and locations:
For Puerto Rico,
February 7, 2011, DoubleTree by
Hilton San Juan, De Diego Avenue,
San Juan, Puerto Rico
¨
February 9, 2011, Mayaguez Holiday
Inn, 2701 Hostos Avenue,
¨
Mayaguez, Puerto Rico
February 10, 2011, Holiday Inn Ponce
& Tropical Casino, 3315 Ponce By
Pass, Ponce, Puerto Rico
For the U.S. Virgin Islands,
February 16, 2011, The Buccaneer
Hotel, Estate Shoys, Christiansted,
St. Croix, U.S. Virgin Islands.
February 17, 2011, Holiday Inn
(Windward Passage Hotel) Charlotte
Amalie, St. Thomas, U.S. Virgin
Islands
All meetings will be held from 7 p.m.
to 10 p.m.
FOR FURTHER INFORMATION CONTACT:
Caribbean Fishery Management Council,
˜
268 Munoz Rivera Avenue, Suite 1108,
San Juan, Puerto Rico 00918–1920,
telephone (787) 766–5926.
SUPPLEMENTARY INFORMATION: The
Caribbean Fishery Management Council
will hold Scoping meetings to receive
public input on the following
SUMMARY:
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management options. The complete
Options Paper is available at: https://
caribbeanfmc.com/pdfs/2011%20ACL%
20Amendment%20Options%20Paper%
20December%2022%202010.pdf:
Management Options
Action 1. Management Reference Points
Action 1a: Establish a year sequence
for determining average annual landings
that can be applied to each island group
for both the commercial and
recreational sectors.
Option 1: No action. Retain current
management reference points or proxies
for species/species groups within the
reef fish, queen conch, lobster, and
corals FMUs.
Option 2: Establish a year sequence
for determining average annual landings
for each species or species group within
Puerto Rico.
Sub-option A: Establish a start year
for the year sequence.
Sub-sub-option i: Use 1983 as the start
date for determining average annual
landings for each species or species
group within Puerto Rico.
Sub-sub-option ii: Use 1998 as the
start date for determining average
annual landings for each species or
species group within Puerto Rico.
Sub-sub-option iii: Use 1999 as the
start date for determining average
annual landings for each species or
species group within Puerto Rico.
Sub-sub-option iv: Use 2000 as the
start date for determining average
annual landings for each species or
species group within Puerto Rico.
Sub-sub-option v: Use 2003 as the
start date for determining average
annual landings for each species or
species group within Puerto Rico.
Sub-sub-option vi: Use 2004 as the
start date for determining average
annual landings for each species or
species group within Puerto Rico.
Sub-option B: Establish an end year
for the year sequence.
Sub-sub-option i: Use 2005 as the end
date for determining average annual
landings for each species or species
group within Puerto Rico.
Sub-sub-option ii: Use 2007 as the
end date for determining average annual
landings for each species or species
group within Puerto Rico.
Sub-sub-option iii: Use 2008 as the
end date for determining average annual
landings for each species or species
group within Puerto Rico.
Option 3: Establish a year sequence
for determining average annual landings
for each species or species group within
St. Thomas and St. John.
Sub-option A: Establish a start year
for the year sequence.
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Sub-sub-option i: Use 2000 as the start
date for determining average annual
landings for each species or species
group within St. Thomas and St. John.
Sub-sub-option ii: Use 2003 as the
start date for determining average
annual landings for each species or
species group within St. Thomas and St.
John.
Sub-option B: Establish an end year
for the year sequence.
Sub-sub-option i: Use 2005 as the end
date for determining average annual
landings for each species or species
group within St. Thomas and St. John.
Sub-sub-option ii: Use 2007 as the
end date for determining average annual
landings for each species or species
group within St. Thomas and St. John.
Option 4: Establish a year sequence
for determining average annual landings
for each species or species group within
St. Croix.
Sub-option A: Establish a start year
for the year sequence.
Sub-sub-option i: Use 1998 as the start
date for determining average annual
landings for each species or species
group within St. Croix.
Sub-sub-option ii: Use 1999 as the
start date for determining average
annual landings for each species or
species group within St. Croix.
Sub-sub-option iii: Use 2000 as the
start date for determining average
annual landings for each species or
species group within St. Croix.
Sub-sub-option iv: Use 2003 as the
start date for determining average
annual landings for each species or
species group within St. Croix.
Sub-option B: Establish an end year
for the year sequence.
Sub-sub-option i: Use 2005 as the end
date for determining average annual
landings for each species or species
group within St. Croix.
Sub-sub-option ii: Use 2007 as the
end date for determining average annual
landings for each species or species
group within St. Croix.
Action 1b. Establish MSY proxy.
The MSA requires that FMPs specify
a number of reference points for
managed fish stocks, including:
• Maximum Sustainable Yield
(MSY)—The greatest amount or yield
that can be sustainably harvested under
prevailing environmental conditions.
• Overfishing Threshold—The
maximum rate of fishing a stock can
withstand (MFMT) or maximum yield a
stock can produce (OFL), annually,
while still providing MSY on a
continuing basis.
• Overfished Threshold (MSST)—The
biomass level below which a stock
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would not be capable of producing
MSY.
• Annual Catch Limit (ACL)—The
annual level to which catch is limited
in order to prevent overfishing from
occurring.
• Optimum Yield (OY)—The amount
or yield that provides the greatest
overall benefit to the Nation, taking into
account food production, recreational
opportunities and the protection of
marine ecosystems.
Together, these parameters are
intended to provide the means to
measure the status and performance of
fisheries relative to established goals.
Available data in the U.S. Caribbean are
not sufficient to support direct
estimation of MSY and other key
parameters. In such cases, the National
Standard 1 (NS1) guidelines direct
regional fishery management councils to
adopt other measures of productive
capacity, including long-term average
catch, which can serve as reasonable
proxies.
Option 1: No action. Retain current
management reference points or proxies
for species/species groups.
Discussion: This alternative would
retain the present MSY proxy, OY, and
overfishing threshold definitions
specified in the Comprehensive SFA
Amendment for species/species groups.
These definitions are detailed in Table
6.
The current MSY proxy is based on
average catch (C) and on estimates of
where stock biomass and fishing
mortality rates are in relation to MSY
levels during the period over which
catches are averaged. The overfishing
threshold (MFMT) is defined as a rate of
fishing which exceeds that which would
produce MSY. And OY is defined as the
amount of fish produced by fishing at a
rate equal to 75% of that which would
produce MSY. The numerical values
associated with these parameters are
provided in Table 6.
TABLE 6—CURRENT MSY PROXY, OY
AND OVERFISHING THRESHOLD DEFINITIONS
FOR
SPECIES/SPECIES
GROUPS—Continued
Reference
point
Overfishing
Threshold.
Optimum Yield
Status quo definition
MFMT = FMSY.
OY = average yield associated with fishing on a continuing basis at FOY;
where FOY = 0.75FMSY.
The Comprehensive SFA Amendment
in which these reference points were
established pre-dated the MSRA
provisions requiring FMPs to specify
ACLs; consequently, the Comprehensive
SFA Amendment did not explicitly
specify this parameter for managed
species/species groups. However, the
ABC estimates derived from the
Council’s MSY control rule could be
considered to represent the ACLs if no
additional action were taken to revise
management reference points in this
amendment.
Option 2: Redefine management
reference points or proxies based on the
time series of catch data that is
considered to be consistently reliable
across all islands as defined in Action
1a.
Discussion: Option 2 would define
aggregate management reference points
or proxies based on what the Council
considers to be the longest time series
of catch data that is consistently reliable
across all islands. Specific definitions
are detailed in Table 7.
The MSY proxy specified by Option
2 would equate to average catch,
calculated using commercial landings
data and recreational landings data
defined in Action 1a. Commercial data
would be derived from trip ticket
TABLE 6—CURRENT MSY PROXY, OY reports collected by the state
AND OVERFISHING THRESHOLD DEFI- governments. Recreational data would
NITIONS
FOR
SPECIES/SPECIES be derived from the MRFSS.
The overfishing threshold (OFL)
GROUPS
would be defined as the amount of catch
Reference
corresponding to the MSY proxy, and
Status quo definition
point
overfishing would be determined to
occur if annual catches exceeded the
Maximum Sus- MSY proxy = C/[(FCURR/
overfishing threshold (Option 2(a)) or if
tainable
FMSY) × (BCURR/BMSY)];
Yield.
where C is calculated
annual catches exceeded the overfishing
based on commercial
threshold and scientists (in consultation
landings for the years
with managers) attributed the overage to
1997–2001 for Puerto
increased catches versus improved data
Rico and 1994–2002 for
collection and monitoring (Option 2(b)).
the USVI, and on rec-
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reational landings for the
years 2000–2001.
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TABLE 7—MANAGEMENT REFERENCE POINTS OR PROXIES PROPOSED UNDER ALTERNATIVE 2
Reference point
Option 2
Maximum Sustainable Yield ........................................
Overfishing Threshold:
Option 2(a) ............................................................
Option 2(b) ............................................................
Optimum Yield/Annual Catch Limit:
Option 2(c) ............................................................
Option 2(d) ............................................................
Option 2(e) ............................................................
Option 2(f) .............................................................
Option 2(g) ............................................................
Option 2(h) ............................................................
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The OY and ACL would be equal
values, and the same socioeconomic and
ecological tradeoffs would be
considered in the determination of
where to set both of these parameters.
Most of the alternative ACL definitions
considered here are more restrictive
than the current OY definition and
would prevent the fishery from
achieving OY as currently defined. ACL
(= OY) Options 2(c) through 2(f) would
set those parameters equal to some
proportion (100–50%) of the OFL to
take into account uncertainty, ecological
factors, and other concerns. Option 2(g)
would set the ACL (= OY) equal to the
ABC recommended by the Council’s
Scientific and Statistical Committee.
Option 2(h) would set the ACL (= OY)
equal to zero for surgeonfish.
Maximum Sustainable Yield (MSY)
The MSY proxy defined by no action
Option 1 averages catches over the
longest time period during which data
were considered to be relatively stable
at the time the Council approved the
Comprehensive SFA Amendment.
Because the Council had fewer years of
catch data to work with at that time, that
proxy incorporated Puerto Rico and
USVI catch data prior to 1999. The MSY
proxies evaluated in Option 2 does not
use pre-1999 data in average catch
calculations because those data were
collected by gear type rather than by
family group. The Council instead
prefers to use data from more recent
years, when the data were collected by
family group and therefore provide a
relatively consistent baseline among all
of the islands.
Additionally, in contrast to the no
action Option 1, Option 2 does not
attempt to incorporate information on
recreational catches in the USVI because
the MRFSS does not provide this
information and no alternative data are
available to reliably estimate these
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MSY proxy = average annual commercial catch selected by Council in Action 1a.
OFL = MSY proxy; overfishing occurs when annual catches exceed the OFL.
OFL = MSY proxy; overfishing occurs when annual catches exceed the OFL, unless
NMFS’ Southeast Fisheries Science Center (in consultation with the Caribbean Fishery
Management Council and its Scientific and Statistical Committee) determines the overage occurred because data collection/monitoring improved, rather than because
catches actually increased.
OY
OY
OY
OY
OY
OY
=
=
=
=
=
=
ACL
ACL
ACL
ACL
ACL
ACL
=
=
=
=
=
=
OFL.
OFL × (0.85).
OFL × (0.75).
OFL × (0.50).
ABC specified by Scientific and Statistical Committee.
0.
landings. As a result, the MSYs
specified by these alternative proxies
are expected to be underestimated to
some unknown degree. In general,
underestimating MSY can result in
foregone yield, whereas overestimating
MSY can lead to overfishing.
Overfishing Threshold (MFMT/OFL)
The overfishing threshold defined by
Option 1 is a maximum fishing
mortality threshold (MFMT) equal to the
fishing mortality rate at MSY. Because
this fishing mortality rate is unknown
for U.S. Caribbean species, the
Comprehensive SFA Amendment
adopted natural mortality rate as a
proxy for this parameter. However, data
are insufficient to evaluate the
sustainability of current fishing
mortality rates relative to this proxy and
make a determination as to whether
overfishing is or is not occurring. To
remedy this, Option 2 proposes to
specify a catch-based, rather than
fishing mortality-based, overfishing
threshold, called the overfishing limit
(OFL). Annual catches would be
evaluated relative to the OFL to
determine whether overfishing is or is
not occurring. This approach is
consistent with the NS1 guidelines,
which provide fishery managers the
flexibility to determine if overfishing
occurs based on either fishing mortality
rates or actual annual catch.
Option 2 would essentially maintain
the same relationship as the no action
alternative between the overfishing
threshold and MSY. MSY represents the
maximum yield a species complex can
provide in the long term, while OFL
estimates the amount of annual catch
above which overfishing is occurring. In
theory, the annual OFL would vary
above and below the MSY level
depending on fluctuations in stock size.
Since both MSY and OFL are related to
the highest fishing mortality rate that
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will not result in overfishing, the longterm average of OFLs would be expected
to equate to MSY, provided that stock
abundance is high enough to support
MSY. But, in practice, the annual OFL
proposed in Option 2 would remain
constant at the MSY level until stock
biomass can be estimated.
Sub-option (a) would result in an
automatic overfishing determination if
annual catch exceeded the OFL in any
given year, whereas Option (b) would
provide scientists (in consultation with
managers) the flexibility to evaluate the
cause of the reported catch increase
prior to making a determination that a
species complex is undergoing
overfishing. Specifically, they would
consider whether the reported increase
represents an actual increase in landings
or just improved data collection and
monitoring. The intent of this suboption is to eliminate any incentive for
fishermen to under-report or misreport
catches to avoid exceeding ACLs and
triggering associated AMs.
Optimum Yield (OY) and Annual Catch
Limits (ACLs)
The current OY defined by no action
Option 1 is derived from the technical
guidance provided by Restrepo et al.
(1998), which recommends the target
fishing mortality rate be set equal to the
average yield available on a continuing
basis from fishing at 75% of the fishing
mortality rate that would produce MSY.
The authors of that guidance indicate
that fishing at this level adds precaution
and maintains stocks at higher biomass
levels, while sacrificing only a small
amount (∼ 6.25%) of catch. Because data
are insufficient to estimate the fishing
mortality rate that would produce MSY,
the Comprehensive SFA Amendment
estimated the OY of each species/
species group to equal 93.75% of MSY.
While the no action Option 1 does not
explicitly define ACLs for the target
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species, the ABC estimates specified by
the Council’s MSY control rule could be
considered to represent the ACLs of
these species/species groups if no
additional action were taken through
this amendment to revise management
reference points. However, these ABC
values are very uncertain as they were
calculated using natural mortality rate
as a proxy for the fishing mortality rate
that would produce MSY and informed
judgment regarding stock biomass. And,
because these values were set well
below MSY values to address SFA
Working Group determinations
regarding overfishing, they would
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prevent the fishery from achieving OY;
even though recent landings data
indicate that, in most cases,
management controls appear to have
effectively reduced catch rates below
the overfishing threshold.
To remedy this, Option 2 would set
the OY and ACL as equal values,
requiring the Council to consider the
socioeconomic and ecological
components of OY when determining
how far ACLs should be reduced below
the overfishing threshold to account for
scientific uncertainty in estimating the
OFL and management uncertainty in
effectively constraining harvest over
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time. This approach leads to OY
estimates for the target species that are
below those estimated in the
Comprehensive SFA Amendment,
regardless of the OY (= ACL) alternative
selected. In contrast, most of the OY
alternatives would result in larger OY
estimates for the grouper and parrotfish
complexes relative to the no action
alternative.
Action 1c. Allocation of ACLs among
island groups.
Option 1: No Action. Maintain U.S.
Caribbean-wide reference points.
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Action 2: Management of Aquarium
Trade Species
Option 1: No action. Do not reevaluate and revise management of
aquarium trade species.
Option 2: Consolidate all aquarium
trade species listed in the Fishery
Management Plan for Corals and Reef
Associated Plants and Invertebrates of
Puerto Rico and the U.S. Virgin Islands
and Reef Fish Fishery Management Plan
of Puerto Rico and the U.S. Virgin
Islands into a single Fishery
Management Plan.
Sub-option A: Move all aquarium
trade species listed in the Fishery
Management Plan for Corals and Reef
Associated Plants and Invertebrates of
Puerto Rico and the U.S. Virgin Islands
into the Reef Fish Fishery Management
Plan of Puerto Rico and the U.S. Virgin
Islands.
Sub-option B: Move all of the
aquarium trade species listed in the Reef
Fish Fishery Management Plan of Puerto
Rico and the U.S. Virgin Islands into the
Fishery Management Plan for Corals and
Reef Associated Plants and Invertebrates
of Puerto Rico and the U.S. Virgin
Islands.
Sub-option C: Move all of the
aquarium trade species listed in both
the Fishery Management Plan for Corals
and Reef Associated Plants and
Invertebrates of Puerto Rico and the U.S.
Virgin Islands, and in the Reef Fish
Fishery Management Plan of Puerto
Rico and the U.S. Virgin Islands, into a
separate Fishery Management Plan
specific to aquarium trade species.
Option 3: Remove aquarium trade
species from both the Fishery
Management Plan for Corals and Reef
Associated Plants and Invertebrates of
Puerto Rico and the U.S. Virgin Islands
and the Reef Fish Fishery Management
Plan of Puerto Rico and the U.S. Virgin
Islands.
Sub-option A: Remove all aquarium
trade species from the Fishery
Management Plan for Corals and Reef
Associated Plants and Invertebrates of
Puerto Rico and the U.S. Virgin Islands
and from the Reef Fish Fishery
Management Plan of Puerto Rico and
the U.S. Virgin Islands and no longer
track their landings.
Sub-option B: Move all aquarium
trade species listed in the Fishery
Management Plan for Corals and Reef
Associated Plants and Invertebrates of
Puerto Rico and the U.S. Virgin Islands
and the Reef Fish Fishery Management
Plan of Puerto Rico and the U.S. Virgin
Islands into the ‘data collection only’
category.
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Sub-option C: Move only those
aquarium trade species listed in either
the Fishery Management Plan for Corals
and Reef Associated Plants and
Invertebrates of Puerto Rico and the U.S.
Virgin Islands or the Reef Fish Fishery
Management Plan of Puerto Rico and
the U.S. Virgin Islands, and for which
landings data are available during the
year sequence chosen in Action 1 above,
into the ‘data collection only’ category.
Remove all remaining aquarium trade
species from either the Fishery
Management Plan for Corals and Reef
Associated Plants and Invertebrates of
Puerto Rico and the U.S. Virgin Islands
or the Reef Fish Fishery Management
Plan of Puerto Rico and the U.S. Virgin
Islands and no longer track their
landings.
Option 4: Transfer management
authority, for all aquarium trade species
listed in either the Fishery Management
Plan for Corals and Reef Associated
Plants and Invertebrates of Puerto Rico
and the U.S. Virgin Islands or the Reef
Fish Fishery Management Plan of Puerto
Rico and the U.S. Virgin Islands, to the
jurisdiction of the appropriate
commonwealth or territory as defined
by Action 3(c) of Amendment 2 to the
Fishery Management Plan for the Queen
Conch Fishery of Puerto Rico and the
U.S. Virgin Islands and Amendment 5 to
the Reef Fish Fishery Management Plan
of Puerto Rico and the U.S. Virgin
Islands.
Table 8. List of all species included in
the Aquarium Trade category in both
the Reef Fish and Coral FMPs. Table
contents are extracted from Table 8 of
the Comprehensive Amendment to the
Fishery Management Plans (FMPs) of
the U.S. Caribbean to Address Required
Provisions of the Magnuson-Stevens
Fishery Conservation and Management
Act (a.k.a. the Comprehensive
Sustainable Fisheries Act Amendment).
Reef Fish FMP
Clepticus parrae, Creole wrasse
Halichoeres garnoti, Yellowhead wrasse
Halichoeres cyanocephalus,
Yellowcheek wrasse
Halichoeres maculipinna, Clown wrasse
Thalassoma bifasciatum, Bluehead
wrasse
Liopropoma rubre, Swissguard basslet
Gramma loreto, Royal gramma
Microspathodon chrysurus, Yellowtail
damselfish
Stegastes adustus, Dusky damselfish
Stegastes partitus, Bicolor damselfish
Stegastes planifrons, Threespot
damselfish
Stegastes leucostictus, Beaugregory
Chaetodon capistratus, Foureye
butterflyfish
Chaetodon aculeatus, Longsnout
butterflyfish
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Chaetodon ocellatus, Spotfin
butterflyfish
Chaetodon striatus, Banded butterflyfish
Serranus baldwini, Lantern bass
Serranus annularis, Orangeback bass
Serranus tabacarius, Tobaccofish
Serranus tigrinus, Harlequin bass
Serranus tortugarum, Chalk bass
Opistognathus aurifrons, Yellowhead
jawfish
Opistognathus whitehursti, Dusky
jawfish
Xyrichtys novacula, Pearly razorfish
Xyrichtys splendens, Green razorfish
Echidna catenata, Chain moray
Gymnothorax funebris, Green moray
Gymnothorax miliaris, Goldentail moray
Elacatinus oceanops, Neon goby
Priolepis hipoliti, Rusty goby
Equetus lanceolatus, Jackknife-fish
Equetus punctatus, Spotted drum
Chromis cyanea, Blue chromis
Chromis insolata, Sunshinefish
Abudefduf saxatilis, Sergeant major
Astrapogon stellatus, Conchfish
Apogon maculatua, Flamefish
Amblycirrhitus pinos, Redspotted
hawkfish
Antennarius spp., Frogfish
Bothus lunatus, Peacock flounder
Chaetodipterus faber, Atlantic spadefish
Canthigaster rostrata, Sharpnose puffer
Centropyge argi, Cherubfish
Diodon hystrix, Porcupinefish
Dactylopterus volitans, Flying gurnard
Heteropriacanthus cruentatus, Glasseye
snapper
Hypoplectrus unicolor, Butter hamlet
Holocanthus tricolor, Rock beauty
Myrichthys ocellatus, Goldspotted eel
Ophioblennius macclurei, Redlip
blenny
Pareques acuminatus, High-hat
Rypticus saponaceus, Greater sopafish
Synodus intermedius, Sand diver
Symphurus diomedianus, Caribbean
tonguefish
Family Syngnathidae, Pipefishes and
Seahorses
Family Ogcocephalidae, Batfish
Family Scorpaenidae, Scorpionfish
Table 8 (continued). List of all species
included in the Aquarium Trade
category in both the Reef Fish and Coral
FMPs. Table contents are extracted from
Table 8 of the Comprehensive
Amendment to the Fishery Management
Plans (FMPs) of the U.S. Caribbean to
Address Required Provisions of the
Magnuson-Stevens Fishery
Conservation and Management Act
(a.k.a. the Comprehensive Sustainable
Fisheries Act Amendment).
Coral FMP
Aphimedon compressa, Erect rope
sponge
Astrophyton muricatum, Giant basket
star
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Alpheaus armatus, Snapping shrimp
Aiptasia tagetes, Pale anemone
Astropecten spp., Sand stars
Analcidometra armata, Swimming
crinoid
Bartholomea annulata, Corkscrew
anemone
Cynachirella alloclada, sponge (no
common name)
Condylactis gigantea, Giant pink-tipped
anemone
Cyphoma gibbosum, Flamingo tongue
Chondrilla nucula, Chicken liver sponge
Diadema antillarum, Long-spined
urchin
Davidaster spp., Crinoids
Discosoma spp., False coral
Echinometra spp., Purple urchin
Eucidaris tribuloides, Pencil urchin
Gonodactylus (Neogonodactylus) spp.,
Smashing mantis shrimp
Geodia neptuni, Potato sponge
Haliclona sp., Finger sponge
Holothuria spp., Sea cucumbers
Hereractis lucida, Knobby anemone
Lima spp., Fileclams
Lima scabra, Rough fileclam
Lytechinus spp., Pin cushion urchin
Lysmata spp., Peppermint shrimp
Linckia guildingii, Common comet star
Lysiosquilla spp., Spearing mantis
shrimp
Lebrunia spp., Staghorn anemone
Mithrax spp., Clinging crabs
Mithrax cinctimanus, Banded clinging
crab
Mithrax sculptus, Green clinging crab
Myriastra sp., sponge (no common
name)
Niphates digitalis, Pink vase sponge
Niphates erecta, Lavender rope sponge
Nemaster spp., Crinoids
Ophiocoma spp., Brittlestars
Ophioderma spp., Brittlestars
Ophioderma rubicundum, Ruby
brittlestar
Oreaster reticulatus, Cushion sea star
Ophidiaster guildingii, Comet star
Oliva reticularis, Netted olive
Octopus spp. (except the Common
octopus, O. vulgaris)
Paguristes spp., Hermit crabs
Paguristes cadenati, Red reef hermit
crab
Percnon gibbesi, Nimble spray crab
Periclimenes spp., Cleaner shrimp
Ricordia florida, Florida false coral
Stichodactyla helianthus, Sun anemone
Spirobranchus giganteus, Christmas tree
worm
Sabellastarte magnifica, Magnificent
duster
Sabellastarte spp., Tube worms
Stenopus scutellatus, Golden shrimp
Stenopus hispidus, Banded shrimp
Stenorhynchus seticornis, Yellowline
arrow crab
Spondylus americanus, Atlantic thorny
oyster
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17:03 Jan 13, 2011
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Spinosella plicifera, Iridescent tube
sponge
Spinosella vaginalis, Lavendar tube
sponge
Tripneustes ventricosus, Sea egg urchin
Thor amboinensis, Anemone shrimp
Tectitethya (Tethya) crypta, sponge (no
common name)
Subphylum Urochordata, Tunicates
Tridachia crispata, Lettuce sea slug
Zoanthus spp., Sea mat
Action 3. Recreational fishery
management.
Action 3a. Separation of recreational
and commercial sectors.
Option 1: No action. Do not specify
sector-specific annual catch limits.
Option 2: Specify separate
commercial and recreational annual
catch limits based on the preferred
management reference point time series.
Action 3b. Recreational Bag Limits
Option 1: No action. Do not establish
bag limit restrictions on recreational
harvest.
Option 2: Specify a 5-fish aggregate
bag limit per person (would not apply
to a fisherman who has a valid
commercial fishing license issued by
Puerto Rico or the USVI).
Option 3: Specify a 2-fish aggregate
bag limit per person (would not apply
to a fisherman who has a valid
commercial fishing license issued by
Puerto Rico or the USVI).
Option 4: Establish a 0-fish aggregate
bag limit per person (would not apply
to a fisherman who has a valid
commercial fishing license issued by
Puerto Rico or the USVI) for species in
the surgeonfish FMU.
Option 5: Establish an aggregate bag
limit of: 10 per fisher including not
more than two surgeonfish per fisher or
six surgeonfish per boat, and 30
aggregate fish per boat on a fishing day
(would not apply to a fisherman who
has a valid commercial fishing license
issued by Puerto Rico or the USVI).
Option 6: Establish an aggregate bag
limit of: Five per fisher including not
more than two surgeonfish per fisher or
six surgeonfish per boat, and 15
aggregate fish per boat on a fishing day
(would not apply to a fisherman who
has a valid commercial fishing license
issued by Puerto Rico or the USVI).
Action 4: Accountability Measures.
Action 4a: Triggering Accountability
Measures.
Option 1: No Action. Do not trigger
AMs.
Option 2: Trigger AMs if the Annual
Catch Limit is exceeded based upon:
Sub-option A: A single year of
landings beginning with landings from
2011.
Sub-option B: A single year of
landings beginning with landings from
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Sfmt 4703
2671
2011, then a 2-year running average of
landings in 2012 (average of 2011+2012)
and thereafter (i.e., 2011, 2011–2012,
2012–2013, etc.).
Sub-option C: A single year of
landings beginning with landings from
2011, a 2-year average of landings in
2012 (average of 2011+2012), then a 3year running average of landings in
2013 (average of 2011+2012+2013) and
thereafter (i.e., 2011, 2011–2012, 2011–
2013, 2012–2014, etc.).
Option 3: Trigger AMs if the annual
catch limit is exceeded as defined below
and NMFS’ SEFSC (in consultation with
the Caribbean Fishery Management
Council and its Scientific and Statistical
Committee) determines the overage
occurred because catches increased
versus data collection/monitoring
improved:
Sub-option A: A single year of
landings effective beginning 2011.
Sub-option B: A single year of
landings effective beginning 2011, then
a 2-year running average of landings
effective 2012 and thereafter (i.e., 2011,
2011–2012, 2012–2013, etc.).
Sub-option C: A single year of
landings effective beginning 2011, a 2year running average of landings
effective 2012, then a 3-year running
average of landings effective 2013 and
thereafter (i.e., 2011, 2011–2012, 2011–
2013, 2012–2014, etc.).
Action 4b: Apply Accountability
Measures.
Option 1: No Action. Do not apply
AMs.
Option 2: If AMs are triggered, then
reduce the length of the fishing season
for that species or species group the year
following the trigger determination by
the amount needed to prevent such an
overage from occurring again. The
needed changes will remain in effect
until modified.
Option 3: If AMs are triggered, then
reduce the length of the fishing season
for that species or species group the year
following the trigger determination by
the amount needed to prevent such an
overage from occurring again and to pay
back the overage. The needed changes
will remain in effect until modified.
Action 5: Framework Measures.
Action 5a: Establish Framework
Measures for the Spiny Lobster FMP.
Option 1: No Action. Do not amend
the framework measures for the Spiny
Lobster FMP.
Option 2: Amend the framework
procedures for the Spiny Lobster FMP to
provide a mechanism to expeditiously
adjust the following reference points
and management measures through
framework action:
a. Quota Requirements
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b. Seasonal Closures
c. Area Closures
d. Fishing Year
e. Trip/Bag Limit
f. Size Limits
g. Gear Restrictions or Prohibitions
h. Total Allowable Catch (TAC)
i. Annual Catch Limits (ACLs)
j. Accountability Measures (AMs)
k. Annual Catch Targets (ACTs)
l. Maximum Sustainable Yield (MSY)
m. Optimum Yield (OY)
n. Minimum Stock Size Threshold
(MSST)
o. Maximum Fishing Mortality
Threshold (MFMT)
p. Overfishing Limit (OFL)
q. Acceptable Biological Catch (ABC)
control rules
r. Actions to Minimize the Interaction of
Fishing Gear with Endangered
Species or Marine Mammals
Option 3: Amend the framework
procedures for the Spiny Lobster FMP to
provide the Council with a mechanism
to expeditiously adjust a subset of
management measures outlined in
Option 2.
Action 5b: Establish Framework
Measures for the Corals and Reef
Associated Plants and Invertebrates
FMP.
Option 1: No Action. Do not amend
the framework measures for the Corals
and Reef Associated Plants and
Invertebrates FMP.
Option 2: Amend the framework
procedures for the Corals and Reef
Associated Plants and Invertebrates
FMP to provide a mechanism to
expeditiously adjust the following
reference points and management
measures through framework action:
a. Quota Requirements
b. Seasonal Closures
c. Area Closures
d. Fishing Year
e. Trip/Bag Limit
f. Size Limits
g. Gear Restrictions or Prohibitions
h. Fishery Management Units (FMUs)
i. Total Allowable Catch (TAC)
j. Annual Catch Limits (ACLs)
k. Accountability Measures (AMs)
l. Annual Catch Targets (ACTs)
m. Maximum Sustainable Yield (MSY)
n. Optimum Yield (OY)
o. Minimum Stock Size Threshold
(MSST)
p. Maximum Fishing Mortality
Threshold (MFMT)
q. Overfishing Limit (OFL)
r. Acceptable Biological Catch (ABC)
control rules
s. Actions to Minimize the Interaction of
Fishing Gear with Endangered
Species or Marine Mammals
Option 3: Amend the framework
procedures for the Corals and Reef
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Associated Plants and Invertebrates
FMP to provide the Council with a
mechanism to expeditiously adjust a
subset of management measures
outlined in Option 2.
Special Accommodations
These meetings are physically
accessible to people with disabilities.
For more information or request for sign
language interpretation and other
auxiliary aids, please contact Mr.
´
Miguel A. Rolon, Executive Director,
Caribbean Fishery Management Council,
˜
268 Munoz Rivera Avenue, Suite 1108,
San Juan, Puerto Rico, 00918–1920,
telephone (787) 766–5926, at least five
days prior to the meeting date.
Dated: January 11, 2011.
Tracey L. Thompson,
Acting Director, Office of Sustainable
Fisheries, National Marine Fisheries Service.
[FR Doc. 2011–712 Filed 1–13–11; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
Science Advisory Board Meeting
Office of Oceanic and
Atmospheric Research (OAR), National
Oceanic and Atmospheric
Administration (NOAA), Department of
Commerce (DOC).
ACTION: Notice of public meeting.
AGENCY:
This notice sets forth the
schedule and proposed agenda of a
forthcoming meeting of the NOAA
Science Advisory Board. The members
will discuss and provide advice on
issues outlined in the agenda below.
DATES: The meeting is scheduled for:
Monday, January 31 from 10–11 a.m.
Eastern Time.
ADDRESSES: Conference call. Public
access is available at: NOAA, SSMC 3,
Room 11836, 1315 East-West Highway,
Silver Spring, MD.
FOR FURTHER INFORMATION CONTACT: Dr.
Cynthia Decker, Executive Director,
Science Advisory Board, NOAA, Rm.
11230, 1315 East-West Highway, Silver
Spring, Maryland 20910. (Phone: 301–
734–1156, Fax: 301–713–1459, E-mail:
Cynthia.Decker@noaa.gov)
SUMMARY:
The
Science Advisory Board (SAB) was
established by a Decision Memorandum
dated September 25, 1997, and is the
only Federal Advisory Committee with
responsibility to advise the Under
Secretary of Commerce for Oceans and
Atmosphere on strategies for research,
SUPPLEMENTARY INFORMATION:
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education, and application of science to
operations and information services.
SAB activities and advice provide
necessary input to ensure that National
Oceanic and Atmospheric
Administration (NOAA) science
programs are of the highest quality and
provide optimal support to resource
management.
Matters To Be Considered: The agenda
for the meeting is as follows:
Date and Time: Monday, January 31
from 10–11 a.m. Eastern Time.
Status: The meeting will be open to
public participation at NOAA, SSMC 3,
Room 11836, 1315 East-West Highway,
Silver Spring, Md. with a 5-minute
public comment period from 10:55–11
a.m. The SAB expects that public
statements presented at its meetings will
not be repetitive of previously
submitted verbal or written statements.
In general, each individual or group
making a verbal presentation will be
limited to a total time of one minute.
Written comments should be received in
the SAB Executive Director’s Office by
January 28, 2011 to provide sufficient
time for SAB review. Written comments
received by the SAB Executive Director
after January 28, 2011, will be
distributed to the SAB, but may not be
reviewed prior to the meeting date.
Agenda
1. Revised proposal from the Working
Group Subcommittee on alignment of
SAB Working Groups.
2. Process of SAB comments on
NOAA Responses to SAB products.
Dated: January 10, 2011.
Mark E. Brown,
Chief Financial Officer/Chief Administrator
Officer, Office of Oceanic and Atmospheric
Research, National Oceanic and Atmospheric
Administration.
[FR Doc. 2011–755 Filed 1–13–11; 8:45 am]
BILLING CODE 3510–KD–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 068–XA145
Caribbean Fishery Management
Council; Public Meeting
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice of a public meeting.
AGENCY:
The Caribbean Fishery
Management Council (Council) in
partnership with the Fisheries
Leadership and Sustainability Forum
SUMMARY:
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Agencies
[Federal Register Volume 76, Number 10 (Friday, January 14, 2011)]
[Notices]
[Pages 2665-2672]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-712]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XA146
Caribbean Fishery Management Council; Scoping Meetings
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice of Scoping Meetings.
-----------------------------------------------------------------------
SUMMARY: The Caribbean Fishery Management Council will hold scoping
meetings to obtain input from fishers, the general public, and the
local agencies representatives on the Options Paper for the
Comprehensive Annual Catch Limit (ACL) Amendment for the U.S. Caribbean
including Amendment 6 to the Reef Fish Fishery Management Plan of
Puerto Rico and the U.S. Virgin Islands; Amendment 2 to the Fishery
Management Plan for Corals and Reef Associated Plants and Invertebrates
of Puerto Rico and the U.S. Virgin Islands; Amendment 5 to the Fishery
Management Plan for the Spiny Lobster Fishery of Puerto Rico and the
U.S. Virgin Islands; Amendment 3 to the Fishery Management Plan for the
Queen Conch Fishery of Puerto Rico and the U.S. Virgin Islands
DATES AND ADDRESSES: The scoping meetings will be held on the following
dates and locations:
For Puerto Rico,
February 7, 2011, DoubleTree by Hilton San Juan, De Diego Avenue,
San Juan, Puerto Rico
February 9, 2011, Mayag[uuml]ez Holiday Inn, 2701 Hostos Avenue,
Mayag[uuml]ez, Puerto Rico
February 10, 2011, Holiday Inn Ponce & Tropical Casino, 3315 Ponce
By Pass, Ponce, Puerto Rico
For the U.S. Virgin Islands,
February 16, 2011, The Buccaneer Hotel, Estate Shoys,
Christiansted, St. Croix, U.S. Virgin Islands.
February 17, 2011, Holiday Inn (Windward Passage Hotel) Charlotte
Amalie, St. Thomas, U.S. Virgin Islands
All meetings will be held from 7 p.m. to 10 p.m.
FOR FURTHER INFORMATION CONTACT: Caribbean Fishery Management Council,
268 Mu[ntilde]oz Rivera Avenue, Suite 1108, San Juan, Puerto Rico
00918-1920, telephone (787) 766-5926.
SUPPLEMENTARY INFORMATION: The Caribbean Fishery Management Council
will hold Scoping meetings to receive public input on the following
management options. The complete Options Paper is available at: https://caribbeanfmc.com/pdfs/2011%20ACL%20Amendment%20Options%20Paper%20December%2022%202010.pdf:
Management Options
Action 1. Management Reference Points
Action 1a: Establish a year sequence for determining average annual
landings that can be applied to each island group for both the
commercial and recreational sectors.
Option 1: No action. Retain current management reference points or
proxies for species/species groups within the reef fish, queen conch,
lobster, and corals FMUs.
Option 2: Establish a year sequence for determining average annual
landings for each species or species group within Puerto Rico.
Sub-option A: Establish a start year for the year sequence.
Sub-sub-option i: Use 1983 as the start date for determining
average annual landings for each species or species group within Puerto
Rico.
Sub-sub-option ii: Use 1998 as the start date for determining
average annual landings for each species or species group within Puerto
Rico.
Sub-sub-option iii: Use 1999 as the start date for determining
average annual landings for each species or species group within Puerto
Rico.
Sub-sub-option iv: Use 2000 as the start date for determining
average annual landings for each species or species group within Puerto
Rico.
Sub-sub-option v: Use 2003 as the start date for determining
average annual landings for each species or species group within Puerto
Rico.
Sub-sub-option vi: Use 2004 as the start date for determining
average annual landings for each species or species group within Puerto
Rico.
Sub-option B: Establish an end year for the year sequence.
Sub-sub-option i: Use 2005 as the end date for determining average
annual landings for each species or species group within Puerto Rico.
Sub-sub-option ii: Use 2007 as the end date for determining average
annual landings for each species or species group within Puerto Rico.
Sub-sub-option iii: Use 2008 as the end date for determining
average annual landings for each species or species group within Puerto
Rico.
Option 3: Establish a year sequence for determining average annual
landings for each species or species group within St. Thomas and St.
John.
Sub-option A: Establish a start year for the year sequence.
[[Page 2666]]
Sub-sub-option i: Use 2000 as the start date for determining
average annual landings for each species or species group within St.
Thomas and St. John.
Sub-sub-option ii: Use 2003 as the start date for determining
average annual landings for each species or species group within St.
Thomas and St. John.
Sub-option B: Establish an end year for the year sequence.
Sub-sub-option i: Use 2005 as the end date for determining average
annual landings for each species or species group within St. Thomas and
St. John.
Sub-sub-option ii: Use 2007 as the end date for determining average
annual landings for each species or species group within St. Thomas and
St. John.
Option 4: Establish a year sequence for determining average annual
landings for each species or species group within St. Croix.
Sub-option A: Establish a start year for the year sequence.
Sub-sub-option i: Use 1998 as the start date for determining
average annual landings for each species or species group within St.
Croix.
Sub-sub-option ii: Use 1999 as the start date for determining
average annual landings for each species or species group within St.
Croix.
Sub-sub-option iii: Use 2000 as the start date for determining
average annual landings for each species or species group within St.
Croix.
Sub-sub-option iv: Use 2003 as the start date for determining
average annual landings for each species or species group within St.
Croix.
Sub-option B: Establish an end year for the year sequence.
Sub-sub-option i: Use 2005 as the end date for determining average
annual landings for each species or species group within St. Croix.
Sub-sub-option ii: Use 2007 as the end date for determining average
annual landings for each species or species group within St. Croix.
Action 1b. Establish MSY proxy.
The MSA requires that FMPs specify a number of reference points for
managed fish stocks, including:
Maximum Sustainable Yield (MSY)--The greatest amount or
yield that can be sustainably harvested under prevailing environmental
conditions.
Overfishing Threshold--The maximum rate of fishing a stock
can withstand (MFMT) or maximum yield a stock can produce (OFL),
annually, while still providing MSY on a continuing basis.
Overfished Threshold (MSST)--The biomass level below which
a stock would not be capable of producing MSY.
Annual Catch Limit (ACL)--The annual level to which catch
is limited in order to prevent overfishing from occurring.
Optimum Yield (OY)--The amount or yield that provides the
greatest overall benefit to the Nation, taking into account food
production, recreational opportunities and the protection of marine
ecosystems.
Together, these parameters are intended to provide the means to
measure the status and performance of fisheries relative to established
goals. Available data in the U.S. Caribbean are not sufficient to
support direct estimation of MSY and other key parameters. In such
cases, the National Standard 1 (NS1) guidelines direct regional fishery
management councils to adopt other measures of productive capacity,
including long-term average catch, which can serve as reasonable
proxies.
Option 1: No action. Retain current management reference points or
proxies for species/species groups.
Discussion: This alternative would retain the present MSY proxy,
OY, and overfishing threshold definitions specified in the
Comprehensive SFA Amendment for species/species groups. These
definitions are detailed in Table 6.
The current MSY proxy is based on average catch (C) and on
estimates of where stock biomass and fishing mortality rates are in
relation to MSY levels during the period over which catches are
averaged. The overfishing threshold (MFMT) is defined as a rate of
fishing which exceeds that which would produce MSY. And OY is defined
as the amount of fish produced by fishing at a rate equal to 75% of
that which would produce MSY. The numerical values associated with
these parameters are provided in Table 6.
Table 6--Current MSY Proxy, OY and Overfishing Threshold Definitions for
Species/Species Groups
------------------------------------------------------------------------
Reference point Status quo definition
------------------------------------------------------------------------
Maximum Sustainable Yield.............. MSY proxy = C/[(FCURR/FMSY) x
(BCURR/BMSY)]; where C is
calculated based on commercial
landings for the years 1997-
2001 for Puerto Rico and 1994-
2002 for the USVI, and on
recreational landings for the
years 2000-2001.
Overfishing Threshold.................. MFMT = FMSY.
Optimum Yield.......................... OY = average yield associated
with fishing on a continuing
basis at FOY; where FOY =
0.75FMSY.
------------------------------------------------------------------------
The Comprehensive SFA Amendment in which these reference points
were established pre-dated the MSRA provisions requiring FMPs to
specify ACLs; consequently, the Comprehensive SFA Amendment did not
explicitly specify this parameter for managed species/species groups.
However, the ABC estimates derived from the Council's MSY control rule
could be considered to represent the ACLs if no additional action were
taken to revise management reference points in this amendment.
Option 2: Redefine management reference points or proxies based on
the time series of catch data that is considered to be consistently
reliable across all islands as defined in Action 1a.
Discussion: Option 2 would define aggregate management reference
points or proxies based on what the Council considers to be the longest
time series of catch data that is consistently reliable across all
islands. Specific definitions are detailed in Table 7.
The MSY proxy specified by Option 2 would equate to average catch,
calculated using commercial landings data and recreational landings
data defined in Action 1a. Commercial data would be derived from trip
ticket reports collected by the state governments. Recreational data
would be derived from the MRFSS.
The overfishing threshold (OFL) would be defined as the amount of
catch corresponding to the MSY proxy, and overfishing would be
determined to occur if annual catches exceeded the overfishing
threshold (Option 2(a)) or if annual catches exceeded the overfishing
threshold and scientists (in consultation with managers) attributed the
overage to increased catches versus improved data collection and
monitoring (Option 2(b)).
[[Page 2667]]
Table 7--Management Reference Points or Proxies Proposed Under
Alternative 2
------------------------------------------------------------------------
Reference point Option 2
------------------------------------------------------------------------
Maximum Sustainable Yield.............. MSY proxy = average annual
commercial catch selected by
Council in Action 1a.
Overfishing Threshold:
Option 2(a)........................ OFL = MSY proxy; overfishing
occurs when annual catches
exceed the OFL.
Option 2(b)........................ OFL = MSY proxy; overfishing
occurs when annual catches
exceed the OFL, unless NMFS'
Southeast Fisheries Science
Center (in consultation with
the Caribbean Fishery
Management Council and its
Scientific and Statistical
Committee) determines the
overage occurred because data
collection/monitoring
improved, rather than because
catches actually increased.
Optimum Yield/Annual Catch Limit:
Option 2(c)........................ OY = ACL = OFL.
Option 2(d)........................ OY = ACL = OFL x (0.85).
Option 2(e)........................ OY = ACL = OFL x (0.75).
Option 2(f)........................ OY = ACL = OFL x (0.50).
Option 2(g)........................ OY = ACL = ABC specified by
Scientific and Statistical
Committee.
Option 2(h)........................ OY = ACL = 0.
------------------------------------------------------------------------
The OY and ACL would be equal values, and the same socioeconomic
and ecological tradeoffs would be considered in the determination of
where to set both of these parameters. Most of the alternative ACL
definitions considered here are more restrictive than the current OY
definition and would prevent the fishery from achieving OY as currently
defined. ACL (= OY) Options 2(c) through 2(f) would set those
parameters equal to some proportion (100-50%) of the OFL to take into
account uncertainty, ecological factors, and other concerns. Option
2(g) would set the ACL (= OY) equal to the ABC recommended by the
Council's Scientific and Statistical Committee. Option 2(h) would set
the ACL (= OY) equal to zero for surgeonfish.
Maximum Sustainable Yield (MSY)
The MSY proxy defined by no action Option 1 averages catches over
the longest time period during which data were considered to be
relatively stable at the time the Council approved the Comprehensive
SFA Amendment. Because the Council had fewer years of catch data to
work with at that time, that proxy incorporated Puerto Rico and USVI
catch data prior to 1999. The MSY proxies evaluated in Option 2 does
not use pre-1999 data in average catch calculations because those data
were collected by gear type rather than by family group. The Council
instead prefers to use data from more recent years, when the data were
collected by family group and therefore provide a relatively consistent
baseline among all of the islands.
Additionally, in contrast to the no action Option 1, Option 2 does
not attempt to incorporate information on recreational catches in the
USVI because the MRFSS does not provide this information and no
alternative data are available to reliably estimate these landings. As
a result, the MSYs specified by these alternative proxies are expected
to be underestimated to some unknown degree. In general,
underestimating MSY can result in foregone yield, whereas
overestimating MSY can lead to overfishing.
Overfishing Threshold (MFMT/OFL)
The overfishing threshold defined by Option 1 is a maximum fishing
mortality threshold (MFMT) equal to the fishing mortality rate at MSY.
Because this fishing mortality rate is unknown for U.S. Caribbean
species, the Comprehensive SFA Amendment adopted natural mortality rate
as a proxy for this parameter. However, data are insufficient to
evaluate the sustainability of current fishing mortality rates relative
to this proxy and make a determination as to whether overfishing is or
is not occurring. To remedy this, Option 2 proposes to specify a catch-
based, rather than fishing mortality-based, overfishing threshold,
called the overfishing limit (OFL). Annual catches would be evaluated
relative to the OFL to determine whether overfishing is or is not
occurring. This approach is consistent with the NS1 guidelines, which
provide fishery managers the flexibility to determine if overfishing
occurs based on either fishing mortality rates or actual annual catch.
Option 2 would essentially maintain the same relationship as the no
action alternative between the overfishing threshold and MSY. MSY
represents the maximum yield a species complex can provide in the long
term, while OFL estimates the amount of annual catch above which
overfishing is occurring. In theory, the annual OFL would vary above
and below the MSY level depending on fluctuations in stock size. Since
both MSY and OFL are related to the highest fishing mortality rate that
will not result in overfishing, the long-term average of OFLs would be
expected to equate to MSY, provided that stock abundance is high enough
to support MSY. But, in practice, the annual OFL proposed in Option 2
would remain constant at the MSY level until stock biomass can be
estimated.
Sub-option (a) would result in an automatic overfishing
determination if annual catch exceeded the OFL in any given year,
whereas Option (b) would provide scientists (in consultation with
managers) the flexibility to evaluate the cause of the reported catch
increase prior to making a determination that a species complex is
undergoing overfishing. Specifically, they would consider whether the
reported increase represents an actual increase in landings or just
improved data collection and monitoring. The intent of this sub-option
is to eliminate any incentive for fishermen to under-report or
misreport catches to avoid exceeding ACLs and triggering associated
AMs.
Optimum Yield (OY) and Annual Catch Limits (ACLs)
The current OY defined by no action Option 1 is derived from the
technical guidance provided by Restrepo et al. (1998), which recommends
the target fishing mortality rate be set equal to the average yield
available on a continuing basis from fishing at 75% of the fishing
mortality rate that would produce MSY. The authors of that guidance
indicate that fishing at this level adds precaution and maintains
stocks at higher biomass levels, while sacrificing only a small amount
(~ 6.25%) of catch. Because data are insufficient to estimate the
fishing mortality rate that would produce MSY, the Comprehensive SFA
Amendment estimated the OY of each species/species group to equal
93.75% of MSY.
While the no action Option 1 does not explicitly define ACLs for
the target
[[Page 2668]]
species, the ABC estimates specified by the Council's MSY control rule
could be considered to represent the ACLs of these species/species
groups if no additional action were taken through this amendment to
revise management reference points. However, these ABC values are very
uncertain as they were calculated using natural mortality rate as a
proxy for the fishing mortality rate that would produce MSY and
informed judgment regarding stock biomass. And, because these values
were set well below MSY values to address SFA Working Group
determinations regarding overfishing, they would prevent the fishery
from achieving OY; even though recent landings data indicate that, in
most cases, management controls appear to have effectively reduced
catch rates below the overfishing threshold.
To remedy this, Option 2 would set the OY and ACL as equal values,
requiring the Council to consider the socioeconomic and ecological
components of OY when determining how far ACLs should be reduced below
the overfishing threshold to account for scientific uncertainty in
estimating the OFL and management uncertainty in effectively
constraining harvest over time. This approach leads to OY estimates for
the target species that are below those estimated in the Comprehensive
SFA Amendment, regardless of the OY (= ACL) alternative selected. In
contrast, most of the OY alternatives would result in larger OY
estimates for the grouper and parrotfish complexes relative to the no
action alternative.
Action 1c. Allocation of ACLs among island groups.
Option 1: No Action. Maintain U.S. Caribbean-wide reference points.
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Action 2: Management of Aquarium Trade Species
Option 1: No action. Do not re-evaluate and revise management of
aquarium trade species.
Option 2: Consolidate all aquarium trade species listed in the
Fishery Management Plan for Corals and Reef Associated Plants and
Invertebrates of Puerto Rico and the U.S. Virgin Islands and Reef Fish
Fishery Management Plan of Puerto Rico and the U.S. Virgin Islands into
a single Fishery Management Plan.
Sub-option A: Move all aquarium trade species listed in the Fishery
Management Plan for Corals and Reef Associated Plants and Invertebrates
of Puerto Rico and the U.S. Virgin Islands into the Reef Fish Fishery
Management Plan of Puerto Rico and the U.S. Virgin Islands.
Sub-option B: Move all of the aquarium trade species listed in the
Reef Fish Fishery Management Plan of Puerto Rico and the U.S. Virgin
Islands into the Fishery Management Plan for Corals and Reef Associated
Plants and Invertebrates of Puerto Rico and the U.S. Virgin Islands.
Sub-option C: Move all of the aquarium trade species listed in both
the Fishery Management Plan for Corals and Reef Associated Plants and
Invertebrates of Puerto Rico and the U.S. Virgin Islands, and in the
Reef Fish Fishery Management Plan of Puerto Rico and the U.S. Virgin
Islands, into a separate Fishery Management Plan specific to aquarium
trade species.
Option 3: Remove aquarium trade species from both the Fishery
Management Plan for Corals and Reef Associated Plants and Invertebrates
of Puerto Rico and the U.S. Virgin Islands and the Reef Fish Fishery
Management Plan of Puerto Rico and the U.S. Virgin Islands.
Sub-option A: Remove all aquarium trade species from the Fishery
Management Plan for Corals and Reef Associated Plants and Invertebrates
of Puerto Rico and the U.S. Virgin Islands and from the Reef Fish
Fishery Management Plan of Puerto Rico and the U.S. Virgin Islands and
no longer track their landings.
Sub-option B: Move all aquarium trade species listed in the Fishery
Management Plan for Corals and Reef Associated Plants and Invertebrates
of Puerto Rico and the U.S. Virgin Islands and the Reef Fish Fishery
Management Plan of Puerto Rico and the U.S. Virgin Islands into the
`data collection only' category.
Sub-option C: Move only those aquarium trade species listed in
either the Fishery Management Plan for Corals and Reef Associated
Plants and Invertebrates of Puerto Rico and the U.S. Virgin Islands or
the Reef Fish Fishery Management Plan of Puerto Rico and the U.S.
Virgin Islands, and for which landings data are available during the
year sequence chosen in Action 1 above, into the `data collection only'
category. Remove all remaining aquarium trade species from either the
Fishery Management Plan for Corals and Reef Associated Plants and
Invertebrates of Puerto Rico and the U.S. Virgin Islands or the Reef
Fish Fishery Management Plan of Puerto Rico and the U.S. Virgin Islands
and no longer track their landings.
Option 4: Transfer management authority, for all aquarium trade
species listed in either the Fishery Management Plan for Corals and
Reef Associated Plants and Invertebrates of Puerto Rico and the U.S.
Virgin Islands or the Reef Fish Fishery Management Plan of Puerto Rico
and the U.S. Virgin Islands, to the jurisdiction of the appropriate
commonwealth or territory as defined by Action 3(c) of Amendment 2 to
the Fishery Management Plan for the Queen Conch Fishery of Puerto Rico
and the U.S. Virgin Islands and Amendment 5 to the Reef Fish Fishery
Management Plan of Puerto Rico and the U.S. Virgin Islands.
Table 8. List of all species included in the Aquarium Trade
category in both the Reef Fish and Coral FMPs. Table contents are
extracted from Table 8 of the Comprehensive Amendment to the Fishery
Management Plans (FMPs) of the U.S. Caribbean to Address Required
Provisions of the Magnuson-Stevens Fishery Conservation and Management
Act (a.k.a. the Comprehensive Sustainable Fisheries Act Amendment).
Reef Fish FMP
Clepticus parrae, Creole wrasse
Halichoeres garnoti, Yellowhead wrasse
Halichoeres cyanocephalus, Yellowcheek wrasse
Halichoeres maculipinna, Clown wrasse
Thalassoma bifasciatum, Bluehead wrasse
Liopropoma rubre, Swissguard basslet
Gramma loreto, Royal gramma
Microspathodon chrysurus, Yellowtail damselfish
Stegastes adustus, Dusky damselfish
Stegastes partitus, Bicolor damselfish
Stegastes planifrons, Threespot damselfish
Stegastes leucostictus, Beaugregory
Chaetodon capistratus, Foureye butterflyfish
Chaetodon aculeatus, Longsnout butterflyfish
Chaetodon ocellatus, Spotfin butterflyfish
Chaetodon striatus, Banded butterflyfish
Serranus baldwini, Lantern bass
Serranus annularis, Orangeback bass
Serranus tabacarius, Tobaccofish
Serranus tigrinus, Harlequin bass
Serranus tortugarum, Chalk bass
Opistognathus aurifrons, Yellowhead jawfish
Opistognathus whitehursti, Dusky jawfish
Xyrichtys novacula, Pearly razorfish
Xyrichtys splendens, Green razorfish
Echidna catenata, Chain moray
Gymnothorax funebris, Green moray
Gymnothorax miliaris, Goldentail moray
Elacatinus oceanops, Neon goby
Priolepis hipoliti, Rusty goby
Equetus lanceolatus, Jackknife-fish
Equetus punctatus, Spotted drum
Chromis cyanea, Blue chromis
Chromis insolata, Sunshinefish
Abudefduf saxatilis, Sergeant major
Astrapogon stellatus, Conchfish
Apogon maculatua, Flamefish
Amblycirrhitus pinos, Redspotted hawkfish
Antennarius spp., Frogfish
Bothus lunatus, Peacock flounder
Chaetodipterus faber, Atlantic spadefish
Canthigaster rostrata, Sharpnose puffer
Centropyge argi, Cherubfish
Diodon hystrix, Porcupinefish
Dactylopterus volitans, Flying gurnard
Heteropriacanthus cruentatus, Glasseye snapper
Hypoplectrus unicolor, Butter hamlet
Holocanthus tricolor, Rock beauty
Myrichthys ocellatus, Goldspotted eel
Ophioblennius macclurei, Redlip blenny
Pareques acuminatus, High-hat
Rypticus saponaceus, Greater sopafish
Synodus intermedius, Sand diver
Symphurus diomedianus, Caribbean tonguefish
Family Syngnathidae, Pipefishes and Seahorses
Family Ogcocephalidae, Batfish
Family Scorpaenidae, Scorpionfish
Table 8 (continued). List of all species included in the Aquarium
Trade category in both the Reef Fish and Coral FMPs. Table contents are
extracted from Table 8 of the Comprehensive Amendment to the Fishery
Management Plans (FMPs) of the U.S. Caribbean to Address Required
Provisions of the Magnuson-Stevens Fishery Conservation and Management
Act (a.k.a. the Comprehensive Sustainable Fisheries Act Amendment).
Coral FMP
Aphimedon compressa, Erect rope sponge
Astrophyton muricatum, Giant basket star
[[Page 2671]]
Alpheaus armatus, Snapping shrimp
Aiptasia tagetes, Pale anemone
Astropecten spp., Sand stars
Analcidometra armata, Swimming crinoid
Bartholomea annulata, Corkscrew anemone
Cynachirella alloclada, sponge (no common name)
Condylactis gigantea, Giant pink-tipped anemone
Cyphoma gibbosum, Flamingo tongue
Chondrilla nucula, Chicken liver sponge
Diadema antillarum, Long-spined urchin
Davidaster spp., Crinoids
Discosoma spp., False coral
Echinometra spp., Purple urchin
Eucidaris tribuloides, Pencil urchin
Gonodactylus (Neogonodactylus) spp., Smashing mantis shrimp
Geodia neptuni, Potato sponge
Haliclona sp., Finger sponge
Holothuria spp., Sea cucumbers
Hereractis lucida, Knobby anemone
Lima spp., Fileclams
Lima scabra, Rough fileclam
Lytechinus spp., Pin cushion urchin
Lysmata spp., Peppermint shrimp
Linckia guildingii, Common comet star
Lysiosquilla spp., Spearing mantis shrimp
Lebrunia spp., Staghorn anemone
Mithrax spp., Clinging crabs
Mithrax cinctimanus, Banded clinging crab
Mithrax sculptus, Green clinging crab
Myriastra sp., sponge (no common name)
Niphates digitalis, Pink vase sponge
Niphates erecta, Lavender rope sponge
Nemaster spp., Crinoids
Ophiocoma spp., Brittlestars
Ophioderma spp., Brittlestars
Ophioderma rubicundum, Ruby brittlestar
Oreaster reticulatus, Cushion sea star
Ophidiaster guildingii, Comet star
Oliva reticularis, Netted olive
Octopus spp. (except the Common octopus, O. vulgaris)
Paguristes spp., Hermit crabs
Paguristes cadenati, Red reef hermit crab
Percnon gibbesi, Nimble spray crab
Periclimenes spp., Cleaner shrimp
Ricordia florida, Florida false coral
Stichodactyla helianthus, Sun anemone
Spirobranchus giganteus, Christmas tree worm
Sabellastarte magnifica, Magnificent duster
Sabellastarte spp., Tube worms
Stenopus scutellatus, Golden shrimp
Stenopus hispidus, Banded shrimp
Stenorhynchus seticornis, Yellowline arrow crab
Spondylus americanus, Atlantic thorny oyster
Spinosella plicifera, Iridescent tube sponge
Spinosella vaginalis, Lavendar tube sponge
Tripneustes ventricosus, Sea egg urchin
Thor amboinensis, Anemone shrimp
Tectitethya (Tethya) crypta, sponge (no common name)
Subphylum Urochordata, Tunicates
Tridachia crispata, Lettuce sea slug
Zoanthus spp., Sea mat
Action 3. Recreational fishery management.
Action 3a. Separation of recreational and commercial sectors.
Option 1: No action. Do not specify sector-specific annual catch
limits.
Option 2: Specify separate commercial and recreational annual catch
limits based on the preferred management reference point time series.
Action 3b. Recreational Bag Limits
Option 1: No action. Do not establish bag limit restrictions on
recreational harvest.
Option 2: Specify a 5-fish aggregate bag limit per person (would
not apply to a fisherman who has a valid commercial fishing license
issued by Puerto Rico or the USVI).
Option 3: Specify a 2-fish aggregate bag limit per person (would
not apply to a fisherman who has a valid commercial fishing license
issued by Puerto Rico or the USVI).
Option 4: Establish a 0-fish aggregate bag limit per person (would
not apply to a fisherman who has a valid commercial fishing license
issued by Puerto Rico or the USVI) for species in the surgeonfish FMU.
Option 5: Establish an aggregate bag limit of: 10 per fisher
including not more than two surgeonfish per fisher or six surgeonfish
per boat, and 30 aggregate fish per boat on a fishing day (would not
apply to a fisherman who has a valid commercial fishing license issued
by Puerto Rico or the USVI).
Option 6: Establish an aggregate bag limit of: Five per fisher
including not more than two surgeonfish per fisher or six surgeonfish
per boat, and 15 aggregate fish per boat on a fishing day (would not
apply to a fisherman who has a valid commercial fishing license issued
by Puerto Rico or the USVI).
Action 4: Accountability Measures.
Action 4a: Triggering Accountability Measures.
Option 1: No Action. Do not trigger AMs.
Option 2: Trigger AMs if the Annual Catch Limit is exceeded based
upon:
Sub-option A: A single year of landings beginning with landings
from 2011.
Sub-option B: A single year of landings beginning with landings
from 2011, then a 2-year running average of landings in 2012 (average
of 2011+2012) and thereafter (i.e., 2011, 2011-2012, 2012-2013, etc.).
Sub-option C: A single year of landings beginning with landings
from 2011, a 2-year average of landings in 2012 (average of 2011+2012),
then a 3-year running average of landings in 2013 (average of
2011+2012+2013) and thereafter (i.e., 2011, 2011-2012, 2011-2013, 2012-
2014, etc.).
Option 3: Trigger AMs if the annual catch limit is exceeded as
defined below and NMFS' SEFSC (in consultation with the Caribbean
Fishery Management Council and its Scientific and Statistical
Committee) determines the overage occurred because catches increased
versus data collection/monitoring improved:
Sub-option A: A single year of landings effective beginning 2011.
Sub-option B: A single year of landings effective beginning 2011,
then a 2-year running average of landings effective 2012 and thereafter
(i.e., 2011, 2011-2012, 2012-2013, etc.).
Sub-option C: A single year of landings effective beginning 2011, a
2-year running average of landings effective 2012, then a 3-year
running average of landings effective 2013 and thereafter (i.e., 2011,
2011-2012, 2011-2013, 2012-2014, etc.).
Action 4b: Apply Accountability Measures.
Option 1: No Action. Do not apply AMs.
Option 2: If AMs are triggered, then reduce the length of the
fishing season for that species or species group the year following the
trigger determination by the amount needed to prevent such an overage
from occurring again. The needed changes will remain in effect until
modified.
Option 3: If AMs are triggered, then reduce the length of the
fishing season for that species or species group the year following the
trigger determination by the amount needed to prevent such an overage
from occurring again and to pay back the overage. The needed changes
will remain in effect until modified.
Action 5: Framework Measures.
Action 5a: Establish Framework Measures for the Spiny Lobster FMP.
Option 1: No Action. Do not amend the framework measures for the
Spiny Lobster FMP.
Option 2: Amend the framework procedures for the Spiny Lobster FMP
to provide a mechanism to expeditiously adjust the following reference
points and management measures through framework action:
a. Quota Requirements
[[Page 2672]]
b. Seasonal Closures
c. Area Closures
d. Fishing Year
e. Trip/Bag Limit
f. Size Limits
g. Gear Restrictions or Prohibitions
h. Total Allowable Catch (TAC)
i. Annual Catch Limits (ACLs)
j. Accountability Measures (AMs)
k. Annual Catch Targets (ACTs)
l. Maximum Sustainable Yield (MSY)
m. Optimum Yield (OY)
n. Minimum Stock Size Threshold (MSST)
o. Maximum Fishing Mortality Threshold (MFMT)
p. Overfishing Limit (OFL)
q. Acceptable Biological Catch (ABC) control rules
r. Actions to Minimize the Interaction of Fishing Gear with Endangered
Species or Marine Mammals
Option 3: Amend the framework procedures for the Spiny Lobster FMP
to provide the Council with a mechanism to expeditiously adjust a
subset of management measures outlined in Option 2.
Action 5b: Establish Framework Measures for the Corals and Reef
Associated Plants and Invertebrates FMP.
Option 1: No Action. Do not amend the framework measures for the
Corals and Reef Associated Plants and Invertebrates FMP.
Option 2: Amend the framework procedures for the Corals and Reef
Associated Plants and Invertebrates FMP to provide a mechanism to
expeditiously adjust the following reference points and management
measures through framework action:
a. Quota Requirements
b. Seasonal Closures
c. Area Closures
d. Fishing Year
e. Trip/Bag Limit
f. Size Limits
g. Gear Restrictions or Prohibitions
h. Fishery Management Units (FMUs)
i. Total Allowable Catch (TAC)
j. Annual Catch Limits (ACLs)
k. Accountability Measures (AMs)
l. Annual Catch Targets (ACTs)
m. Maximum Sustainable Yield (MSY)
n. Optimum Yield (OY)
o. Minimum Stock Size Threshold (MSST)
p. Maximum Fishing Mortality Threshold (MFMT)
q. Overfishing Limit (OFL)
r. Acceptable Biological Catch (ABC) control rules
s. Actions to Minimize the Interaction of Fishing Gear with Endangered
Species or Marine Mammals
Option 3: Amend the framework procedures for the Corals and Reef
Associated Plants and Invertebrates FMP to provide the Council with a
mechanism to expeditiously adjust a subset of management measures
outlined in Option 2.
Special Accommodations
These meetings are physically accessible to people with
disabilities. For more information or request for sign language
interpretation and other auxiliary aids, please contact Mr. Miguel A.
Rol[oacute]n, Executive Director, Caribbean Fishery Management Council,
268 Mu[ntilde]oz Rivera Avenue, Suite 1108, San Juan, Puerto Rico,
00918-1920, telephone (787) 766-5926, at least five days prior to the
meeting date.
Dated: January 11, 2011.
Tracey L. Thompson,
Acting Director, Office of Sustainable Fisheries, National Marine
Fisheries Service.
[FR Doc. 2011-712 Filed 1-13-11; 8:45 am]
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