ICES Advice on fishing opportunities, catch, and effort Celtic Seas and Greater North Sea ecoregions Published 30 June 2016 ...
ICES
Advice on fishing opportunities, catch, and effort
Celtic
Seas and Greater North Sea ecoregions Published
30 June 2016
- Sea bass (Dicentrarchus labrax) in divisions 4.b–c, 7.a, and 7.d–h (central and southern North Sea, Irish Sea, English Channel, Bristol Channel, and Celtic Sea)
ICES stock
advice
ICES advises that when the precautionary approach is applied, there
should be zero catch (commercial and recreational) in 2017.
Stock
development over time
SSB peaked in 2010 and has been declining since. Spawning-stock
biomass (SSB) is now below Blim.
The fishing mortality (F) shows an increasing trend but has declined
slightly in recent years. Recruitment has been very poor since 2008;
however, the 2013 estimate shows above-average recruitment.
Figure 5.3.57.1 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h. Summary of stock
assessment (weights in thousand tonnes). Total landings,
including commercial
landings and recreational estimates. Fishing mortality is shown for
the combined commercial and recreational fisheries. Predicted
recruitment values are not shaded.
Stock and
exploitation status
Table
5.3.57.1 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h. State of the stock and
fishery relative to reference points (RP).
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Fishing
pressure
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Stock
size
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2013
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2014
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2015
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2014
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2015
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2016
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Maximum
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FMSY
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Undefined
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MSY
Btrigger
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Below
trigger
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sustainable
yield
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Reduced
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Precautionary
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Fpa,
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Undefined
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Bpa,
Blim
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approach
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Flim
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reproductive
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Management
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FMGT
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-
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-
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-
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Not
applicable
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SSBMGT
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-
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-
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-
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Not
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plan
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applicable
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Qualitative
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Above
any
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-
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-
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-
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Not
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evaluation
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candidate
RP
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applicable
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ICES Advice 2016, Book 5 |
1
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Catch options
Table
5.3.57.2 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h. The basis for the catch
options.
Variable
|
Value
|
Notes
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Source
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F ages 5–11
(2016)
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0.30
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F2015.
Commercial fishery F = 0.22; recreational fishery F = 0.08.
|
ICES (2016a)
|
SSB (2017)
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6
219 t
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Short-term
forecast
|
ICES (2016a)
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Rage
0 (2014, 2015, and
2016)
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6
469 thousands
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Geometric
mean 1985–2013
|
ICES (2016a)
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Total catch
(2016)
|
Unknown
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Total landings
(2016)
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2
305 t
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Commercial
+ recreational
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ICES (2016a)
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Discards
(2016)
|
Unknown
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Table 5.3.57.3 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h. The catch options.
Weights are in tonnes. The option of TAC changes are not
presented, since there
is no TAC for sea bass.
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Total
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Commercial
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Recreational
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Commercial
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%SSB
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landing
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Total F
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Recreational
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SSB
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Rationale |
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landings
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landings
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Basis
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F
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change
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s
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(2017)
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F
(2017)
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(2018)
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(2017)
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(2017)
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(2017)
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*
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(2017)
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Precautionary |
0
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0
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0
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F
= 0
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0
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0
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0
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7583
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21.9
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approach |
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MSY |
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FMSY
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approach# |
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2036
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1475
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560
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F2016
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0.30
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0.22
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0.08
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5845
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−6.0
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SSB2018
=
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Blim
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SSB2018
=
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Other |
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Bpa
= MSY
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Btrigger
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options^ |
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1672
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1212
|
460
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0.8
× F2016
|
0.24
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0.18
|
0.07
|
6152
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−1.1
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1483
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1074
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408
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0.7
x F2016
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0.21
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0.15
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0.06
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6312
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1.5
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1288
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933
|
355
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0.6
× F2016
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0.18
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0.13
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0.05
|
6478
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4.2
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882
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639
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243
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0.4
× F 2016
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0.12
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0.09
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0.03
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6824
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9.7
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453
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328
|
125
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0.2
× F. 2016
|
0.06
|
0.04
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0.02
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7192
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15.6
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*SSB in 2018 relative to
SSB in 2017. |
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# The MSY approach option
was left blank because FMSY
has not been appropriately defined. |
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^The Blim,
Bpa,
and MSY Btrigger
options were left blank because Blim
cannot be achieved in 2018 even with zero catch advice. |
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Basis of the advice |
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Table 5.3.57.4 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h. The basis of the
advice. |
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Advice
basis
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Precautionary
approach.
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Management
plan
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There
is no management plan for sea bass in this area.
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Quality of the
assessment
There are uncertainties in the assessment because of inaccuracies in
the catch data, particularly recreational catches. The point estimate
of 1500 tonnes for the recreational catch is based on different
surveys over a few years, and the assumption of using a constant F to
reconstruct the time-series of catches adds uncertainty to the
assessment. Fishery sampling rates over time have been variable for
all countries.
The estimates of F and SSB have been rescaled as a result of the
addition of age and length composition data introduced during the
recent inter-benchmark (ICES, 2016b). The overall trends remain
similar.
The two survey data series for the eastern English Channel, which is
only a small part of the total stock area, provide good estimation of
recruitment. However, a change in vessel and survey design in the
Channel Ground Fish Survey led to the 2015
2 ICES
Advice 2016, Book 5
value not being included in this
assessment. The very weak recruitment from 2008 to 2012 estimated in
the assessment is confirmed by the surveys and by reduced catches of
young fish by the UK and French fisheries. All the input data to the
assessment and additional information (catch per unit effort in the
French fishery) are indicative of a declining trend of biomass.
Stock identity remains poorly understood and tagging studies are
ongoing. Survival rates of sea bass discarded from commercial vessels
or released by anglers are poorly known.
Figure 5.3.57.2 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h. Historical assessment
results (includes assumed long-term average recruitment
for 2013 onwards in
both assessments). The basis of the assessment changed in 2015 when
the stock was benchmarked (ICES, 2015b).
Issues relevant for the advice
The emergency measures in 2015 reduced pelagic trawl catches of
seabass and also bycatch of seabass in other fisheries. The fishing
mortality in 2016 is assumed to be the same as in 2015 in the catch
forecast and the results show that even with zero catch in 2017 the
stock will stay below Blim
in 2018. However, additional management measures have been introduced
for 2016 which may result in fishing mortality below the assumed. A
sensitivity analysis carried out by ICES indicates that with 30%
reduction in F in 2016, which is considered plausible given the
additional management measures for 2016, and zero catch in 2017 the
stock would increase to just above Blim
in 2018. Given that the stock would be estimated to remain near Blim
and taking into account the uncertainties in the assessment and
forecast, ICES considers that its advice for zero catch in 2017,
aiming to bring the stock above Blim
in the short term, remains valid even if such a decrease in F in 2016
occurs.
Only Blim
and Bpa reference points
were re-estimated this year.
A new benchmark is to be conducted for
seabass in 2017.
Reference points
Table
5.3.57.5 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h.
Reference points, values, and their technical basis.
|
Framework |
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Reference |
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Value
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Technical basis |
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Source
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point |
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MSY |
|
MSY Btrigger |
|
12673
t
|
|
Bpa |
|
ICES
(2016a)
|
|||||
|
approach |
|
FMSY |
|
Not
defined.
|
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|||
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Precautionary |
|
Blim |
|
8075
t
|
|
Lowest observed
spawning-stock biomass. |
|
ICES
(2016a)
|
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Bpa |
|
12673
t
|
|
Blim
× exp(1.645 × σ); σ = 0.274 |
|
ICES
(2016a)
|
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|
approach |
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Flim |
|
Not
defined.
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Fpa |
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Not
defined.
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Management |
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SSBMGT |
|
Not
applicable.
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|
plan |
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FMGT |
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Not
applicable.
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ICES
Advice 2016, Book 5 3
Basis of the
assessment
Table
5.3.57.6 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h. The basis of the
assessment.
|
ICES stock data category |
||
|
Assessment type |
|
Age-
and length-based analytical assessment (Stock Synthesis 3; NOAA
Toolbox) that uses landings in the
|
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model
and in the forecast.
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Commercial
landings (international landings, ages and length frequencies
from catch sampling); one
|
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recruit
survey (UK Solent autumn survey); one bottom trawl survey
(Channel Groundfish Survey); growth
|
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Input data |
|
and
maturity data from sampling of commercial catches and surveys;
natural mortality (inferred from life
|
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history
parameters and maximum observed ages); recreational fishing
mortality estimated for 2012
|
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inferred
from recreational fishery surveys (since 2009).
|
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Discards and bycatch |
|
Discarding
is known to take place but cannot be fully quantified (in the
order of 5% in weight).
|
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Indicators |
|
Catch
per unit effort in the French fishery
|
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Other information |
|
This
stock was benchmarked in 2012, 2014 and 2016 (ICES, 2012, 2014,
2016b). A new benchmark is
|
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planned
for 2017.
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Working group |
Information
from stakeholders
The North Western Waters Advisory Council (NWWAC) framework for
advice for seabass management in Northwestern waters was communicated
to the European Commission on 16th of May 2016 (NWWAC, 2016).
History of the
advice, catch, and management
Table 5.3.57.7 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h. History of ICES advice,
the agreed TAC, and the official and ICES estimates of
commercial landings.
Weights are in thousand tonnes.
|
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Official
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Predicted
catch
|
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ICES
commercial
|
||
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||||
Year
|
ICES
advice
|
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|
Agreed
TAC
|
commercial
|
|
|||
|
corresp. to
advice*
|
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|
landings
|
|||||
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landings
|
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2000
|
-
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-
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|
none
|
2.1
|
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2.4
|
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2001
|
-
|
-
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|
none
|
2.2
|
2.5
|
|
||
2002
|
No
increase in effort or F
|
-
|
|
none
|
2.4
|
2.6
|
|
||
2003
|
No
increase in effort or F
|
-
|
|
none
|
2.9
|
3.4
|
|
||
2004
|
No
increase in effort or F
|
-
|
|
none
|
3.0
|
3.7
|
|
||
2005
|
-
|
-
|
|
none
|
3.2
|
4.4
|
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||
2006
|
-
|
-
|
|
none
|
3.4
|
4.5
|
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||
2007
|
-
|
-
|
|
none
|
3.5
|
4.2
|
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||
2008
|
-
|
-
|
|
none
|
3.0
|
4.2
|
|
||
2009
|
-
|
-
|
|
none
|
4.3
|
4.0
|
|
||
2010
|
-
|
-
|
|
none
|
4.9
|
4.8
|
|
||
2011
|
-
|
-
|
|
none
|
3.9
|
3.9
|
|
||
2012
|
No
increase in catch
|
-
|
|
none
|
3.9
|
4.1
|
|
||
2013
|
20%
reduction in catches (last 3 years’ average)
|
<
6.0**
|
|
none
|
4.1
|
4.1
|
|
||
|
36%
reduction in commercial landings (20%
|
|
|
|
|
|
|
|
|
2014
|
reduction,
followed by 20% precautionary
|
<
2.707**
|
|
none
|
2.8
|
2.7
|
|
||
|
reduction)
|
|
|
|
|
|
|
|
|
2015
|
MSY
approach
|
<
1.155***
|
|
none
|
2.1
|
2.0
|
|
||
2016
|
MSY
approach
|
|
≤ 0.541***
|
|
none
|
|
|
|
|
2017
|
Precautionary
approach
|
0
|
|
|
|
|
|
|
- Advice prior to 2014 was given for sea bass in the Northeast Atlantic.
- Commercial landings.
- Total landings (commercial and recreational landings).
4 ICES
Advice 2016, Book 5
History of
catch and landings
Table
5.3.57.8 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h.
Catch distribution by fleet in 2015 as estimated by ICES.
|
Total catch
|
|
|
|
Commercial
landings
|
|
|
|
|
Commercial
|
|
|
Commercial
|
|
|
Recreational
catch
|
|
|||
|
|
|
|
|
|
|
|
landings
other
|
|
|
|
|
|
|||||||
|
(2015)
|
|
|
|
|
UK
and France
|
|
|
|
|
|
|
discards
|
|
|
(partially
reported)
|
|
|||
|
|
|
|
|
|
|
|
|
countries
|
|
|
|
|
|
||||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
pelagic
|
bottom
|
|
fixed/drift
|
|
|
other
|
|
|
|
|
|
|
|
Known to be substantial
but |
||
|
|
|
|
pair
|
|
|
lines
|
|
all
gears
|
|
|
|
|
cannot be fully quantified |
||||||
|
|
|
|
trawlers
|
|
nets
|
|
gears
|
|
|
|
|
|
|||||||
|
|
|
|
trawlers
|
|
|
|
|
|
|
|
Unknown (in |
|
(surveys indicate total
annual |
||||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||
|
Unknown
|
5%
|
36%
|
|
22%
|
|
20%
|
4%
|
|
13%
|
|
|
the order of |
|
removals by France, UK |
|||||
|
|
|
|
|
|
|
|
5% in weight) |
|
(England), Netherlands,
and |
||||||||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Belgium to the order of
1500 |
|
|
|
|
|
|
|
|
2040
tonnes
|
|
|
|
|
|
|
|
|
|
||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
tonnes in 2012) |
||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Table 5.3.57.9 Sea
bass in divisions 4.b–c, 7.a,
and 7.d–h.
History of commercial landings; both the official and ICES estimated
values are presented
for each country participating in the fishery (in tonnes). Source:
Official landings statistics 1950–2014
and provisional data for 2015, ICES, Copenhagen.
|
Year
|
Belgium
|
Denmark
|
|
Germany
|
France*
|
|
UK
|
|
Netherlands
|
Channel
Is.
|
|
Total
|
Total
ICES
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1985
|
0
|
0
|
|
0
|
620
|
|
105
|
|
0
|
18
|
|
743
|
994
|
|
1986
|
0
|
0
|
0
|
841
|
124
|
0
|
15
|
980
|
1319
|
||||
|
1987
|
0
|
0
|
0
|
1226
|
123
|
0
|
14
|
1363
|
1980
|
||||
|
1988
|
0
|
18
|
0
|
714
|
173
|
8
|
12
|
925
|
1239
|
||||
|
1989
|
0
|
2
|
0
|
675
|
192
|
2
|
48
|
919
|
1161
|
||||
|
1990
|
0
|
0
|
0
|
609
|
189
|
0
|
25
|
824
|
1063
|
||||
|
1991
|
0
|
0
|
0
|
726
|
239
|
0
|
16
|
982
|
1227
|
||||
|
1992
|
0
|
0
|
0
|
721
|
148
|
0
|
36
|
906
|
1186
|
||||
|
1993
|
0
|
1
|
0
|
718
|
230
|
0
|
45
|
994
|
1255
|
||||
|
1994
|
0
|
1
|
0
|
593
|
535
|
0
|
49
|
1178
|
1371
|
||||
|
1995
|
0
|
1
|
0
|
801
|
708
|
0
|
69
|
1579
|
1835
|
||||
|
1996
|
0
|
1
|
0
|
1703
|
563
|
8
|
56
|
2331
|
3022
|
||||
|
1997
|
0
|
1
|
0
|
1429
|
561
|
1
|
74
|
2066
|
2620
|
||||
|
1998
|
0
|
2
|
0
|
1363
|
488
|
48
|
79
|
1980
|
2390
|
||||
|
1999
|
0
|
1
|
0
|
NA
|
685
|
32
|
108
|
826
|
2670
|
||||
|
2000
|
0
|
5
|
0
|
1522
|
407
|
60
|
130
|
2124
|
2407
|
||||
|
2001
|
0
|
2
|
0
|
1619
|
458
|
77
|
80
|
2236
|
2500
|
||||
|
2002
|
0
|
1
|
0
|
1580
|
627
|
96
|
73
|
2377
|
2622
|
||||
|
2003
|
154
|
1
|
0
|
1903
|
586
|
163
|
84
|
2891
|
3458
|
||||
|
2004
|
159
|
1
|
0
|
1883
|
617
|
191
|
159
|
3010
|
3731
|
||||
|
2005
|
206
|
1
|
0
|
1937
|
512
|
327
|
220
|
3203
|
4430
|
||||
|
2006
|
211
|
2
|
0
|
2033
|
574
|
308
|
162
|
3290
|
4377
|
||||
|
2007
|
178
|
1
|
0
|
1975
|
713
|
376
|
142
|
3385
|
4064
|
||||
|
2008
|
188
|
0
|
0
|
1420
|
791
|
380
|
123
|
2902
|
4107
|
||||
|
2009
|
173
|
0
|
0
|
2732
|
697
|
395
|
91
|
4088
|
3889
|
||||
|
2010
|
215
|
4
|
0
|
3294
|
736
|
399
|
120
|
4768
|
4563
|
||||
|
2011
|
152
|
2
|
0
|
2566
|
793
|
395
|
90
|
3998
|
3858
|
||||
|
2012
|
154
|
3
|
0
|
2399
|
892
|
376
|
55
|
3879
|
3987
|
||||
|
2013
|
145
|
5
|
2
|
2786
|
803
|
370
|
37
|
4148
|
4136
|
||||
|
2014
|
146
|
1
|
0
|
1309
|
1038
|
253
|
37
|
2784
|
2682
|
||||
|
2015**
|
40
|
0
|
0
|
1110
|
683
|
207
|
26
|
2066
|
2040
|
- Landings since 2000 are ICES estimates.
- Preliminary.
ICES
Advice 2016, Book 5 5
Table 5.3.57.10 Sea
bass in divisions 4.b–c, 7.a, and 7.d–h. History of recreational
catch and landings estimates provided to ICES by area for
each country which has
conducted surveys of the fishery. RSE = relative standard error.
|
|
Country
|
|
|
Year
|
|
|
Area
|
|
|
Weight
/
|
|
|
|
Kept
|
|
|
RSE
|
|
|
|
Released
|
|
|
RSE
|
|
|
Total
|
|
|
|
RSE
|
|
|
Release
|
|
|
|
|
|
|
|
|
|
Number
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
rate
|
|
|||||||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||
|
|
|
|
|
|
|
|
Northeast |
|
Weight |
|
|
2343
t
|
-
|
|
|
830
t
|
|
|
|
|
3173
t
|
26%
|
|
26%
|
|
||||||||||
|
|
|
|
|
|
|
|
Atlantic |
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||||
|
|
|
|
|
2009–
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||
|
|
|
|
|
|
ICES |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||
|
|
France
|
2011*,**
|
|
|
|
Weight |
|
|
940
t
|
|
|
|
|
|
332
t
|
|
|
|
|
1272
t
|
>26%
|
|
26%
|
|
|||||||||||
|
|
|
|
|
|
Subareas 4 & |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||||||||||||
|
|
|
|
|
|
|
7
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
2011–2012
|
|
Northeast |
|
Weight |
|
|
3146
t
|
-
|
|
|
776
t
|
|
|
|
|
3922t
|
-
|
20%
|
|
||||||||||||
|
|
|
|
|
|
Atlantic |
|
|
|
|
|
|
|
|
|
|
||||||||||||||||||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||||||||||||
|
|
|
|
|
March
|
|
North Sea |
|
Number |
234000
|
38%
|
|
131000
|
27%
|
|
366000
|
30%
|
|
64%
|
|
||||||||||||||||
|
|
|
|
|
2010–Feb
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
North Sea |
|
Weight*** |
|
|
138
t
|
37%
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||
|
|
Netherland
|
2011
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||||||
|
|
s
|
|
March
|
|
North Sea |
|
Number |
335000
|
26%
|
|
332000
|
21%
|
|
667000
|
17%
|
|
50%
|
|
|||||||||||||||||
|
|
|
|
|
2012–Feb
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
North Sea |
|
Weight*** |
|
|
229
t
|
26%
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||
|
|
|
|
2013
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||
|
|
UK
|
|
|
|
ICES
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
380–690
|
|
|
|
|
|
|
|
||||
|
|
2012^
|
|
Subareas
4 &
|
Weight
|
|
|
230–440
t
|
|
|
|
|
|
150–250
t
|
|
|
|
|
|
|
26–38%
|
|
36–39%
|
|||||||||||||
|
|
(England)
|
|
|
|
|
|
|
|
|
|
|
|
|
t
|
|
|
|
||||||||||||||||||
|
|
|
|
|
7
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||||||||||
|
|
Belgium
|
2013
|
|
|
North Sea |
|
Weight |
|
|
60
t
|
-
|
|
-
|
|
-
|
|
-
|
-
|
|
-
|
|
- ~ 80% by weight in 2009/2011 was recreational sea angling.
- RSE was 26% for subareas 7 and 8 combined; Subarea 7 represented 40% of the total.
- 93% by weight in 2010/2011 is recreational sea angling; 2012/2013 estimates are sea angling only. ^ Survey covered only recreational sea angling.
Summary of the
assessment
Table
5.3.57.11 Sea
bass in divisions 4.b–c, 7.a,
and 7.d–h.
Assessment summary.
|
|
|
|
Recruitment
|
|
|
|
|
|
|
|
|
SSB
|
|
|
|
|
|
|
|
|
Landings
|
|
|
Mean
F
|
|
|
Year
|
|
|
Age 0
|
|
|
High
|
|
|
Low
|
|
|
|
|
High
|
|
|
Low
|
|
|
|
|
|
|||
|
|
|
|
|
|
|
|
|
tonnes
|
|
|
|
|
|
|
tonnes
|
|
|
Ages
5–11
|
|
||||||
|
|
|
|
thousands
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1985
|
|
355
|
688
|
22
|
13506
|
15916
|
11095
|
|
2216
|
0.151
|
||||||||||||||||
1986
|
|
686
|
1304
|
68
|
12242
|
14455
|
10029
|
|
2441
|
0.181
|
||||||||||||||||
1987
|
|
7868
|
10019
|
5717
|
11155
|
13170
|
9140
|
|
3041
|
0.241
|
||||||||||||||||
1988
|
|
6188
|
8980
|
3395
|
10154
|
11975
|
8332
|
|
2286
|
0.183
|
||||||||||||||||
1989
|
|
37654
|
42653
|
32655
|
10054
|
11767
|
8340
|
|
2149
|
0.181
|
||||||||||||||||
1990
|
|
3213
|
5675
|
750
|
9481
|
11179
|
7783
|
|
1930
|
0.185
|
||||||||||||||||
1991
|
|
6106
|
8685
|
3527
|
8497
|
10200
|
6794
|
|
1987
|
0.218
|
||||||||||||||||
1992
|
|
9044
|
11823
|
6265
|
7507
|
9186
|
5827
|
|
1935
|
0.217
|
||||||||||||||||
1993
|
|
4163
|
6297
|
2030
|
7738
|
9372
|
6104
|
|
2196
|
0.2
|
||||||||||||||||
1994
|
|
13202
|
16811
|
9593
|
9710
|
11260
|
8160
|
|
2689
|
0.167
|
||||||||||||||||
1995
|
|
20048
|
23846
|
16249
|
12825
|
14363
|
11286
|
|
3359
|
0.181
|
||||||||||||||||
1996
|
|
1024
|
1984
|
65
|
14725
|
16362
|
13087
|
|
4527
|
0.249
|
||||||||||||||||
1997
|
|
23272
|
27659
|
18885
|
14309
|
16016
|
12601
|
|
4027
|
0.238
|
||||||||||||||||
1998
|
|
8440
|
12906
|
3975
|
13592
|
15343
|
11842
|
|
3728
|
0.232
|
||||||||||||||||
1999
|
|
22970
|
28426
|
17514
|
13219
|
15001
|
11437
|
|
4042
|
0.248
|
||||||||||||||||
2000
|
|
11067
|
15228
|
6906
|
13313
|
15122
|
11503
|
|
3861
|
0.222
|
||||||||||||||||
2001
|
|
12605
|
17961
|
7250
|
14090
|
15985
|
12195
|
|
4005
|
0.222
|
||||||||||||||||
2002
|
|
20114
|
26871
|
13357
|
14768
|
16768
|
12767
|
|
4232
|
0.219
|
||||||||||||||||
2003
|
|
21068
|
27267
|
14869
|
15807
|
17900
|
13714
|
|
5162
|
0.254
|
6 ICES
Advice 2016, Book 5
|
|
|
|
Published
30 June 2016
|
||||||
|
|
|
|
|
|
|
|
|
|
|
2004
|
13829
|
18886
|
8772
|
16458
|
18622
|
14294
|
5516
|
0.259
|
|
|
|
2005
|
10283
|
14278
|
6288
|
17024
|
19247
|
14802
|
6208
|
0.292
|
|
|
2006
|
11175
|
15204
|
7147
|
16759
|
19062
|
14455
|
6120
|
0.294
|
|
|
2007
|
8606
|
12416
|
4796
|
16619
|
19001
|
14236
|
5869
|
0.273
|
|
|
2008
|
5362
|
8575
|
2150
|
17294
|
19779
|
14810
|
6009
|
0.264
|
|
|
2009
|
4508
|
6922
|
2094
|
18021
|
20710
|
15331
|
5810
|
0.252
|
|
|
2010
|
865
|
1739
|
0
|
18215
|
21217
|
15213
|
6386
|
0.291
|
|
|
2011
|
2845
|
4533
|
1158
|
17001
|
20386
|
13616
|
5536
|
0.275
|
|
|
2012
|
1595
|
2812
|
378
|
15738
|
19578
|
11899
|
5487
|
0.305
|
|
|
2013
|
10576
|
20107
|
1046
|
13781
|
18125
|
9438
|
5383
|
0.36
|
|
|
2014
|
6469*
|
|
|
11057
|
15896
|
6219
|
3680
|
0.313
|
|
|
2015
|
6469*
|
|
|
9084
|
14348
|
3820
|
2839
|
0.303
|
|
|
2016
|
6469*
|
|
|
7320
|
12874
|
1765
|
|
|
|
|
Average
|
9942
|
13812
|
6790
|
13158
|
15631
|
10685
|
4021
|
0.241
|
|
- Long-term geometric mean.
- Annual recreational landings consistent with recreational F(5–11) of 0.08, estimated by assessment model.
Sources and
references
EU. 2015. Council Regulation (EU) 2015/104 of 19 January 2015 fixing
for 2015 the fishing opportunities for certain fish stocks and groups
of fish stocks, applicable in Union waters and, for Union vessels, in
certain non-Union waters, amending Regulation (EU) No 43/2014 and
repealing Regulation (EU) No 779/2014
EU. 2016. How is the EU protecting sea bass? Online article
available at:
http://ec.europa.eu/fisheries/cfp/fishing_rules/sea-bass/index_en.htm.
[Accessed 1
June 2016].
ICES. 2012. Report of the Inter-Benchmark Protocol on New Species
(Turbot and Sea Bass; IBPNew 2012), 1–5 October 2012, Copenhagen,
Denmark. ICES CM 2012/ACOM:45. 239 pp.
ICES. 2014. Report of the Inter-Benchmark Protocol for Sea Bass in
the Irish Sea, Celtic Sea, English Channel, and Southern North Sea
(IBP–Bass). By correspondence. ICES CM 2014/ACOM:45. 218 pp.
ICES. 2016a. Report of the Working Group for the Celtic Seas
Ecoregion (WGCSE), 4–13 May 2016, ICES Headquarters, Copenhagen,
Denmark. ICES CM 2016/ACOM:13.
ICES. 2016b. Report of the Second Inter-Benchmark Protocol for Sea
Bass in the Irish Sea, Celtic Sea, English Channel, and Southern
North Sea (IBP–Bass2). By correspondence. ICES CM 2016/ ACOM:31.
191 pp.
ICES. 2016c.
Advice basis. In Report of the ICES Advisory Committee, 2016.
ICES Advice 2016, Book 1, Section 1.2.
NWWAC. 2016. Framework for advice – Seabass management in North
Western Waters; 13 May 2016. North Western Waters Advisory Council.
http://www.nwwac.org/_fileupload/Opinions%20and%20Advice/Year%2011/Seabass/NWWAC_Framework_advice_Seabass_May-2016_EN.pdf.
ICES
Advice 2016, Book 5 7
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