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Total Allowable Catch |
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At its Sixteenth annual meeting, the CCSBT agreed that the status of
the southern bluefin tuna (SBT) stock was at a critical stage and
that a meaningful reduction in the total allowable catch (TAC) was
necessary in order to recover the stock and work toward reaching an
interim rebuilding target reference point of 20% of the original
spawning stock. Consequently, the CCSBT reduced the SBT global total
allowable catch (TAC) for 2010 and 2011 to an average level over the
two years of 80% of the previously allocated global TAC of 11,810
tonnes. Accordingly, the average global TAC for each of the 2010 and
2011 fishing seasons will be 9,449 tonnes. The allocation of the TAC
amongst Members and Cooperating Non-Members for the 2010 and 2011
fishing seasons is specified below (in tonnes). To help ensure
compliance with the TAC, the CCSBT also adopted a
Resolution on Actions Plans to Ensure Compliance with Conservation
and Management Measures
(PDF 22Kb):-
Members (for the 2010 and 2011 fishing seasons)
The “Nominal Catch” listed below is the catch before any reductions
are applied, the “Allocated Catch” is the reduced catch allocated
for 2010 and 2011 and the “Effective Catch Limit” is the effective
catch after additional agreed voluntary reductions have been
applied.
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|
Nominal
Catch |
Allocated
Catch |
Effective
Catch Limit |
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Japan |
5,665 |
2,261 |
2,261 |
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Australia |
5,665 |
4,270 |
4,015 |
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Republic of Korea |
1,140 |
859 |
859 |
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Fishing Entity of Taiwan |
1,140 |
859 |
859 |
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New Zealand |
1000 |
754 |
709 |
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Indonesia |
750 |
651 |
651 |
Cooperating Non-Members (for 2010)
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Philippines |
45 |
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South Africa |
40 |
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European Community |
10 |
In addition to the reduced TAC, the CCSBT decided that it would work
toward implementing a management procedure (MP) in 2011 and that the
MP would be the basis for TAC setting in 2012 and beyond. An
emergency rule will be developed as part of the MP for exceptional
circumstances such as recruitment levels lower than historically low
levels. Finally, the CCSBT has agreed to set a TAC of 5,000t-6,000t
for the 2012 fishing season in the event that an MP cannot be
finalised by 2012, unless the Extended Commission decides otherwise
based upon the new stock assessment.
More complete information on the total catch and its allocation is
provided in paragraphs 45 to 61 and Attachment 13 of the
CCSBT16 Report
(PDF 815Kb).

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Stock Assessment |
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A summary of the stock assessment and stock status results from the
2009 meeting of the CCSBT’s Extended Scientific Committee (ESC) is
as follows:-
- During 2009, the SBT operating model used in 2008 was revised
and run under a number of scenarios to project future stock status
under different constant annual catches. The scenarios all
indicated that the spawning stock biomass remains at a very low
level: typically about 5% or less of the original spawning stock
biomass, which is a little more than 15% of the spawning stock
biomass that would produce the maximum sustainable yield. There
was no sign of the spawning stock rebuilding.
- Recruitments during the last two decades were estimated to be
well below the levels over 1950-1980. Recruitment in the 1990s
fluctuated at a low level without any overall trend, but
recruitments for 2000 to 2002 were poor. The two following year
classes were somewhat stronger, though still below the average
1990s level. Recruitments since 2005 cannot be estimated precisely
as yet. Although some data gave positive signals, it remained
probable that at least some of these year classes were as weak as
in 2000-2002. As the weak year classes in 2000-2002 move into the
spawning stock over the next few years, there will be a negative
impact on the spawning stock biomass.
- The median projections under the 2007-2009 TAC (of 11810t) for
the base case scenario showed a decline in spawning stock biomass
in the short term (to 2013), and remain below the current level in
the longer term (to at least 2025). The same was true for nearly
all of the other plausible scenarios considered. To rebuild the
spawning stock and thereby also reduce the risk in the short term
of further poor recruitments, a reduction to the 2007-2009 TAC is
required.
- While rebuilding of the spawning stock would almost certainly
increase sustainable yield, the risks that this rebuilding might
be jeopardised by further poor recruitments have probably
increased since the last assessment. Because the spawning stock
biomass is very low, it may not provide security against adverse
environmental effects leading to a few years of poor recruitment.
Short-term projections for the spawning stock biomass are
relatively reliable because the year classes that will shortly
join the spawning stock have already been observed in the fishery.
However, longer term projections are more uncertain as they depend
on future recruitments whose levels have to be determined by use
of an estimated stock-recruitment relationship, and so should be
treated with greater caution in terms of their implications for
appropriate future catch limits.
A summary of the advice from the 2009 ESC meeting is that:-
- Positive factors affecting sustainability of future catches
are:
- the reported catch has reduced over recent years;
- indicators and the assessment suggest that the 2003 and 2004
year classes are not as low as the weak 2000, 2001, and 2002
year classes; and
- indicators of age 4+ SBT have exhibited some recent upward
trends.
- However, there remain serious sources of concern from new and
previous information including:
- a very low spawning stock (about 5% of the original spawning
stock and 15% of the spawning stock biomass that would produce
the maximum sustainable yield);
- the three poor recruitments from 2000 to 2002, and
indications of some further poor recruitments after 2004, which
will lead to a further decline in spawning stock biomass;
- a general decline in recruitment since about 1970,
coincident with declining spawning stock sizes; and
- current fishing mortality is nearly double FMSY.
- A meaningful reduction in catch should be effected below the
current 2007-2009 TAC of 11810t.
- Noting the CCSBT’s intent to adopt a Management Procedure (MP)
at its 2010 annual meeting, and given the high probability that
such a MP will require catch and effort data as inputs, steps
should be taken to ensure accurate future catch and effort
reporting.

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Management Procedure |
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An initial meeting was held to steer the Commission's course on
a management strategy in May 2000 in Tokyo, Japan. The Commission
agreed that a procedure should be developed as a set of rules, agreed
in advance, to dictate how a Total Allowable Catch for the SBT fishery
would be adjusted as data becomes available. The management procedure
will have three components: (1) a list of data as inputs, (2) an
algorithm or model to process the data and (3) rules to translate
the algorithm output into a Total Allowable Catch.
From March 2002 to September 2005, the CCSBT developed an
operating model for the SBT fishery, tested several candidate
decision rules and finally selected a management procedure for the
fishery. However, reviews of SBT data during 2006
suggested that southern bluefin tuna catches may have been
substantially under-reported over the previous 10-20 years. The
impact of unreported catches on the estimates of past total catch
and CPUE meant that it was not possible to proceed with the chosen
Management Procedure, and that the Management Procedure needed to be
re-evaluated.
Work has recommenced on developing a management procedure and it
is planned that the management procedure be finalised in 2010 for
implementation in 2011 and that it be the basis for TAC setting from
2012 and beyond.

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Trade
Management |
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The CCSBT implemented a Trade
Information Scheme (PDF 1635Kb) (TIS)
on 1 June 2000 to collect more accurate and comprehensive data on
SBT fishing through monitoring trade. The TIS also operates to deter
Illegal, Unreported and Unregulated (IUU) fishing by effectively
denying access to markets for SBT. From 1 January 2010, the
CCSBT Catch Documentation Scheme (CDS) comes into effect and from
that time, CDS documents will be issued for all trade of SBT instead
of TIS documents. The CDS will also cover domestic landings of SBT.
The core of the TIS is the provision for all Members and Cooperating
Non-Members of the CCSBT to maintain requirements for all imports of
SBT to be accompanied by a completed CCSBT Statistical Document. The
Document must be endorsed by an authorised competent authority in
the exporting country and includes extensive details of the shipment
such as name of fishing vessel, gear type, area of catch, dates,
etc. Shipments not accompanied by this form must be denied entry by
the Member country. Completed forms are lodged with the CCSBT
Secretariat and are used to maintain a database for monitoring
catches and trade. Reconciliation of these forms is conducted
against electronic lists of exports submitted by CCSBT Members and
Cooperating Non-Members.
The Scheme requires the Document to include the country of destination
and to set minimum standards for completion of TIS documents. The
requirement to include destination country was made in the light of
markets for SBT developing outside CCSBT Members. The CCSBT is also
seeking the Cooperation of Non-Member importing countries with the TIS
aims. The United States has passed domestic legislation to recognise
CCSBT documents with effect from 1 July 2005, which brings trade to
the United States under the provisions of the CCSBT Scheme.
See the
Data section of this website for the
published subset of TIS data.

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Catch Documentation Scheme |
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The CCSBT Catch Documentation Scheme (CDS) comes into effect on 1
January 2010 and replaces the existing TIS system. The CDS provides
for tracking and validation of legitimate SBT product flow from catch
to the point of first sale on domestic or export markets. As part of
the CDS, all transhipments, landings of domestic product, exports,
imports and re-exports of SBT must be accompanied by the appropriate
CCSBT CDS Document(s), which will include a Catch Monitoring Form and
possibly a Re-Export/Export After Landing of Domestic Product Form.
Similarly, transfers of SBT into and between farms must be documented
on either a Farm Stocking Form or a Farm Transfer Form as appropriate.
In addition, each whole SBT that is transhipped, landed as domestic
product, exported, imported or re-exported must have a uniquely
numbered tag attached to it and the tag numbers of all SBT (together
with other details) will be recorded on a Catch Tagging Form. Copies
of all documents issued and received will be provided to the CCSBT
Secretariat on a quarterly basis for compiling to an electronic
database, analysis, identification of discrepancies, reconciliation
and reporting.
Full details of the CCSBT CDS are available from the
Resolution on the implementation of a CCSBT Catch Documentation Scheme
(PDF 426Kb).

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Monitoring of SBT Transhipments at Sea |
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The CCSBT Transhipment monitoring program came into effect on 1
April 2009. The program applies to transhipments at sea from tuna
longline fishing vessels with freezing capacity (referred to as
“LSTLVs”). It requires, amongst other things, for carrier vessels that
receive SBT transhipments at sea from LSTLVs to be authorised to
receive such transhipments and for a CCSBT observer to be on board the
carrier vessel during the transhipment. The CCSBT transhipment program
is harmonised and operated in conjunction with those of ICCAT and IOTC
to avoid duplication of the same measures. ICCAT or IOTC observers on
a transhipment vessel that is authorised to receive SBT are deemed to
be CCSBT observers provided that the CCSBT standards are met.
Full details of the CCSBT transhipment program are available from
the
Resolution on establishing a Program for Transhipment by Large-Scale
Fishing Vessels
(PDF 28Kb).

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List of Approved Vessels and Farms |
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The CCSBT has established records for:
Members and Cooperating Non-Members of the CCSBT will not allow the
landing or trade etc. of SBT caught by fishing vessels and farms, or
transhipped to carrier vessels that are not on these lists..

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Vessel Monitoring System |
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The CCSBT Vessel Monitoring System (VMS) came into effect
immediately after the Fifteenth Annual Meeting of the Commission, on
17 October 2008. It requires CCSBT Members and Cooperating
Non-Members to adopt and implement satellite-linked VMS for vessels
fishing for SBT that complies with the IOTC, WCPFC, CCAMLR, or ICCAT
VMS requirements according to the respective convention area in
which the SBT fishing is being conducted. For fishing outside of
these areas, the IOTC VMS requirements must be followed.
Full details of the CCSBT VMS are available from the
Resolution on establishing the CCSBT Vessel Monitoring System
(15Kb).

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Action Plan |
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In the past, significant and increasing volumes of SBT were
being taken by flag of convenience vessels. This had been of major
concern to the CCSBT where the stock needs to be carefully managed
and where the actions of these vessels undermines the conservation
measures already taken by Members. The Commission has sought the
cooperation of these countries in supporting its management and
conservation measures. They have also been advised that if cooperation
is not forthcoming, the Commission will consider measures, including
trade restrictive measures, to be taken against them in accordance
with the
Action
Plan (PDF 7Kb)
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