Europaudvalget 2018
KOM (2018) 0452
Offentligt
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EUROPEAN
COMMISSION
Brussels, 11.6.2018
SWD(2018) 329 final
COMMISSION STAFF WORKING DOCUMENT
Accompanying the document
COMMUNICATION FROM THE COMMISSION
on the State of Play of the Common Fisheries Policy and Consultation on the Fishing
Opportunities for 2019
{COM(2018) 452 final}
EN
EN
kom (2018) 0452 - Ingen titel
Contents
Contents ..................................................................................................................................... 1
I. State of stocks ......................................................................................................................... 2
II. Specific actions for the Mediterranean and Black Seas ...................................................... 13
III. Report on the balance between fishing capacity and fishing opportunities ....................... 16
IV. Economic performance of the EU fishing fleet ................................................................ 27
V. The implementation of the Landing Obligation .................................................................. 35
1
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I. State of stocks
This section explains in detail the progress made on achieving maximum sustainable yield
(F
MSY
) and the situation of stocks.
1. Progress report
Each year, the Commission requests the Scientific, Technical and Economic Committee for
Fisheries (STECF) to measure the progress made on achieving F
MSY
in line with the
objectives of the Common Fisheries Policy (CFP). The exploitation rate relative to F
MSY
is
calculated by the STECF, the International Council for the Exploration of the Sea (ICES) and
the General Fisheries Commission for the Mediterranean (GFCM).
In line with recommended best practice, all historical data series have been updated. This
means that some new methods have been introduced, new science taken into account, and
new data added.
The main findings of the STECF technical report
1
are summarised below.
1.1 Knowledge of the state of stocks
1.1.1 ICES area
2
The number of stocks for which there is scientific advice about fishing mortality compared to
the fishing mortality that would lead to the MSY has remained stable in general at 66. The
slight decrease in the number of F
MSY
assessed stocks from 2015 to 2016 is due to a
methodological change made by the STECF, whereby stocks with less than 5 years of data
were not included in the analysis.
1
2
2018-XX_STECF XX-XX:
Monitoring the performance of the Common Fisheries Policy (WP).
Reference to the ICES area or "North-East Atlantic" covers FAO area 27 and includes the waters of the Baltic
Sea, North Sea, Irish Sea, Celtic Sea and adjacent waters.
2
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Figure 1 Number of stocks in the ICES area for which estimates of F/F
MSY
are available
by year
Table 1 Number of stocks in the ICES area for which estimates of F/F
MSY
are available by
ecoregion and year
Ecoregion
ALL
Baltic Sea
BoBiscay & Iberia
Celtic Seas
Greater North Sea
Widely distributed
2003
66
8
9
21
21
7
2004
65
8
9
20
21
7
2005
66
8
9
21
21
7
2006
67
8
9
22
21
7
2007
67
8
9
22
21
7
2008
67
8
9
22
21
7
2009
68
8
9
23
21
7
2010
67
8
9
22
21
7
2011
69
8
9
23
22
7
2012
70
8
9
24
22
7
2013
71
8
9
25
22
7
2014
71
8
9
25
22
7
2015
71
8
9
25
22
7
2016
66
8
9
23
22
4
1.1.2. Mediterranean Sea and Black Sea
In the Mediterranean and Black Sea, there was a strong increasing trend in the number of
stocks assessed between 2003 and 2009, up from 22 to 47; the number of stock assessments
remained stable until 2014, then decreased to 39 in 2015 and 21 in 2016. For 2016, there are
no results for any of the GFCM stock assessments and the indicator values for 2016 are based
on the results of only 22 stock assessments. As a result, the values are not comparable with
those of previous years. Hence in Figure 2, the 2016 value is represented as stand-alone, and
the indicators are plotted up to 2015 only.
3
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Figure 2 Number of stock assessments in the Mediterranean a and Black Sea by year.
The totals include stocks in the following GSAs only: 1, 5-7, 9, 10-19, 22-23, 25 and 29.
1.2. Fishing compared to the maximum sustainable yield rate (F
MSY
)
4
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1.2.1
North-East Atlantic
On trends in F/F
MSY,
fishing pressure in the ICES area is decreasing steadily with the
indicator value close to 1 in 2016; this means that over all stocks, on average, the exploitation
levels are close to F
MSY
. In the ICES area, among the 65 to 71 stocks that are fully assessed
over the years, the proportion of overexploited stocks decreased from more than 70% to close
to 40% over the last 10 years.
Figure 3 F/F
MSY
trend
Figure 4 Number of stocks by year for which fishing mortality (F) exceeded F
MSY
.
Figure 5 Number of stocks by year and ecoregion for which fishing mortality (F)
exceeded F
MSY
.
5
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Table 2. Number of stocks by year and ecoregion for which fishing mortality (F)
exceeded F
MSY
.
Ecoregion
ALL
Baltic Sea
BoBiscay & Iberia
Celtic Seas
Greater North Sea
Widely distributed
2003
46
7
6
13
13
7
2004
45
6
6
12
16
5
2005
50
6
7
14
18
5
2006
49
6
7
14
18
4
2007
51
6
8
16
17
4
2008
48
6
6
16
16
4
2009
39
6
5
13
12
3
2010
39
6
5
12
12
4
2011
32
4
5
10
10
3
2012
37
5
5
12
13
2
2013
28
3
6
8
9
2
2014
32
2
6
8
13
3
2015
29
4
5
8
10
2
2016
29
4
5
9
9
2
Figure 6 Number of stocks by year for which fishing mortality (F) did not exceed F
MSY
.
6
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Figure 7 Number of stocks by year and ecoregion for which fishing mortality (F) did not
exceed F
MSY
.
Table 3 Number of stocks by year and ecoregion for which fishing mortality (F) did not
exceed F
MSY
Ecoregion
ALL
Baltic Sea
BoBiscay & Iberia
Celtic Seas
Greater North Sea
Widely distributed
2003
20
1
3
8
8
0
2004
20
2
3
8
5
2
2005
16
2
2
7
3
2
2006
18
2
2
8
3
3
2007
16
2
1
6
4
3
2008
19
2
3
6
5
3
2009
29
2
4
10
9
4
2010
28
2
4
10
9
3
2011
37
4
4
13
12
4
2012
33
3
4
12
9
5
2013
43
5
3
17
13
5
2014
39
6
3
17
9
4
2015
42
4
4
17
12
5
2016
42
4
4
16
13
5
1.2.2. Mediterranean and Black Seas
In the Mediterranean and Black Sea, the trends in F/F
MSY
show a median level slightly
varying around 2.3 from 2003 to 2015, with no decreasing trend.
Figure 8 F/F
MSY
trend
7
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1.3 Biomass trends
In ICES area
3
the Spawning Stock Biomass (SSB) has been genereally increasing since
2006 and was around 39% higher on average in 2016 than in 2003.
Figure 9 Trend in SSB relative to 2003 in the North East Atlantic
3
Reference to the ICES area or "North-East Atlantic" covers FAO area 27 and includes the waters of the Baltic
Sea, North Sea, Irish Sea, Celtic Sea and adjacent waters.
8
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For the Mediterranean and Black Seas,
the level of uncertainty makes it difficult to
conclude anything about trend. The situation remains more or less unchanged since the start
of the series in 2003.
Figure 10 SSB trend relative to 2003 in the Mediterranean and Black Sea
In outermost regions,
the Commission has identified
4
the need for Member States to set up
the collection of fisheries scientific data and adopt management measures in line with the
CFP to ensure the long-term
sustainable development of Outermost regions’ fisheries.
2. Setting fishing opportunities
For 2018 the number of total allowables catches (TACs) set in line with F
MSY
increased from
44 in 2017 to 53
5
in 2018, representing 69% of the F
MSY
assessed TACs fished in the North-
East Atlantic, North Sea and Baltic Sea. Of the overall expected catches for 2018, around
12% do not have F
MSY
advice, but are assessed by ICES based on precautionary advice.
During the discussions with Member States socio-economic considerations have been taken
into account, with Member States sending detailed submissions to the Commission.
Communication on “A stronger and renewed partnership with the EU’s Outermost regions”, COM(2017)623
final of 24.10.2017.
5
A TAC is considered in line with MSY if it is at or below the MSY TAC advised by ICES and if its biomass is
above Btrigger. An example of a TAC not listed on the MSY list in 2018 is western Baltic cod, Although the
TAC is in line with MSY 2018, its biomass is below Btrigger.
4
9
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Table 4: TACs with F
MSY
advice (volume)
TACs with MSY advice (volume)
2010
2012
2013
2014
% share of TACs in
50%
45%
49%
48%
line with MSY advice
(volume)
% share of TACs not
in line with MSY
22%
23%
21%
22%
advice (volume)
% share of TACs
28%
33%
30%
30%
without MSY advice
2015
51%
2016
55%
2017
61%
2018
60%
20%
29%
20%
25%
19%
20%
27%
13%
Table 5: TACs with F
MSY
advice (volume in tonnes)
EU stocks
Total TAC volume
(MSY assessed stocks)
TAC volume fished at
F
MSY
TAC volume not fished
at F
MSY
% fished at F
MSY
% not fished at F
MSY
1.613.861
1.567.277
46.584
97%
3%
EU/NO jointly
managed stocks Coastal state stocks
773.444
632.999
140.445
82%
18%
891.474
28.319
863.151
3%
97%
Total
3.278.779
2.228.595
1.043.583
69%
31%
Table 6: Number of TACs with F
MSY
advice
6
Number of TACs with MSY advice
2005
TACs with MSY
34
advice
TACs set in
2
accordance with or
lower than advice
TACs set above
32
advice
% of TACs in
accordance with or
6%
lower than advice
2007
32
2
30
6%
2008
33
4
29
12%
2009
35
5
30
14%
2010
39
11
28
28%
2011
35
13
22
37%
2012
38
20
18
53%
2013
41
25
16
61%
2014
46
27
19
59%
2015
62
36
30
58%
2016
72
36
36
50%
2017
75
44
31
59%
2018
76
54
23
71%
6
Figures for 2005-2017 are taken from previous Communications.
10
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The following paints a more detailed picture for each sea basin:
The
Baltic Sea
is the sea basin with the longest experience of Member States and
stakeholders working together on fisheries management measures in regionalisation.
Considerable effort has been put into developing new gears and putting them in place
through joint recommendations that are sent to the Commission. The result of the
commitment of stakeholders and Member States to sustainable fisheries management can
be seen in the responsible decisions taken on the TACs for 2018. These followed the
Baltic Sea multiannual plan with 7 out of 8 TACs, for which we receive F
MSY
advice set in
line with F
MSY
. In terms of volume of landings this means thatv 95% of the total catch in
the Baltic Sea is from sustainably managed stocks in line with F
MSY
, while 4% is from
TACs where we have precautionary advice.
Herring and sprat were set in line with F
MSY
, and the TAC for the main basin salmon was
set below F
MSY
. The TAC for western cod was rolled over for 2018. TAC reductions were
adopted for eastern cod (-8%) and Gulf of Riga herring (-7%) under the precautionary
approach, and for Gulf of Finland salmon (-5%). The main basin salmon TAC follows the
F
MSY
approach and is kept at a low level to help improve stocks in the weakest salmon
rivers. In 2017, the Torneälven river was found to have the largest returns of wild Atlantic
salmon in the world, thanks to sustainable management.
In the
North Sea, Skagerrak and Kattegat,
for the F
MSY
assessed stocks that are
managed by the EU alone, 99.7% of expected landings are from sustainably managed
stocks. Thanks to the F
MSY
successes in the North Sea we increased TACs for cod in the
North Sea by 10% and in the Skagerrak by 39%. Thanks to F
MSY
management TACs were
increased for nephrops by 22% and for haddock by 23%. The TAC for sole was decreased
by 4%. These examples of F
MSY
management translate into higher and sustainable
incomes for the fishing industry. Turbot and brill represent another positive development
with the combined TAC increased by 44 % in line with scientific advice.
In
North-Western Waters,
for the F
MSY
assessed stocks that are managed by the EU
alone, 94% of the expected landings are from sustainably managed stocks.
This sea basin also boasts important success stories that poove that we are on the right
track. Examples are sole stocks in the Channel, where TACs increased by 2 % for the
Western Channel and by 25% for the Eastern Channel in line with F
MSY
in 2018. The
positive development for Eastern Channel sole is a major achievement of the Advisory
Council, who agreed a management approach for this stock in 2015. It is thanks to this
that Eastern Channel sole is nowadays a F
MSY
success story. Northern hake continues to be
the biggest demersal TAC and was decreased by 7% to keep it in line with F
MSY
.
There was also a significant improvement in the Celtic Sea, with the TAC for cod
increasing by 9% and being managed in line with F
MSY
in 2018. However, cod is also part
of a wider mixed fishery, where the setting of fishing opportunities for other stocks such
as haddock and whiting remains challenging. Improvements are needed to increase
selectivity as part of the package to prevent the early disruption of fishing opportunities
with the implementation of the landing obligation in 2019. Seabass management has been
11
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challenging, with further, worrying decreases in the stock biomass; this calls for even
more restrictive measures on both commercial fishing and recreational angling. While
stringent in the short-term, these measures agreed at the Council should allow this iconic
species to recover.
The
nephrops
fishery in the Celtic Sea is another F
MSY
success story with an increase of
TAC by 15% in the Irish and Celtic Seas. In the Irish Sea there was also a positive story
in the recovery of cod, which has seen a 376% increase in the TAC in line with F
MSY
after
several years of low biomass. Haddock and herring will also be fished at F
MSY
with a 23%
and 70% increase respectively in their TACs. All of these increases again translate
directly into higher and sustainable incomes for the fishing industry.
For
South-Western Waters,
of the F
MSY
assessed stocks that are managed by the EU
alone, 90% of expected landings come from sustainably managed stocks. An important
success story for this sea basin is the Advisory Council management approach to Bay of
Biscay sole which delivered a 6% increase in the TAC and a first ever listing of F
MSY
thanks to the efforts of the stakeholders. TACs were agreed in line with F
MSY
for Iberian
anglerfish and horse mackerel, Bay of Biscay anglerfish and horse mackerel, nephrops,
sole and megrim. The TACs for horse mackerel and megrim in the Bay of Biscay were
increased by 20% and 21% respectively in line with F
MSY
. For megrim and Norway
lobster in the Bay of Biscay, both TACs were reduced in line with scientific advice to
maintain F
MSY
status, as was the TAC for Iberian waters horse mackerel (-20%). Southern
hake saw a 12% decrease in the TAC with the aim of achieving F
MSY
in 2019. Anchovy
and anglerfish in the Bay of Biscay continue to be fished sustainably with unchanged
TAC levels. All of the increases again translate into higher and sustainable incomes for
the fishing industry.
For
deep-sea stocks,
fishing opportunities make up less than 1% of all landings in the
EU. They are fixed under a two-year cycle and TACs were set in November 2016 for
2017 and 2018. Roundnose grenadier in North Western Waters, was set in accordance
with F
MSY
. All other stocks are data- or assessment-limited.
For
stocks subject to Coastal States consultations
1 out of 10 TACs, for which we
receive F
MSY
advice, are set in line with F
MSY
, namely Atlanto-Scandian herring. This
represents 3% in terms of volume of landings of all Coastal States TACs. While
achieving F
MSY
by 2020 for all Coastal States stocks will be difficult, it is the
Commission's objective to make as much progress as possible together with our
international partners the Faroe Islands, Norway and Russia on achieving F
MSY
also for
these stocks.
12
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II. Specific actions for the Mediterranean and Black Seas
In recent years the Commission has stepped-up its efforts to advance towards sustainable
exploitation levels of marine resources in the Mediterranean and Black Seas, which are
threatened by intense overfishing. In particular, the signature of the
‘Malta MedFish4Ever
Declaration’
in March 2017 created a new strategic framework for fisheries governance in
the region and a set of five actions with measurable deliverables for the next 10 years
7
.
Increased cooperation and political engagement enshrined in the Declaration have also helped
make concrete progress.
The main achievements are summarized below.
A. Within the framework of the GFCM
At the 41st session of the GFCM (October 2017, Montenegro), 8 EU proposals were adopted
as binding recommendations. The adopted proposals covered three main areas: fisheries
conservation, control and Illegal, Unreported and Uregulated (IUU) fishing activities and data
collection. This includes:
On fisheries conservation: (i) a regional adaptive management plan for the
exploitation of red coral in the Mediterranean Sea; (ii) a fisheries restricted area
in the Jabuka/Pomo Pit in the Adriatic Sea; (iii) the management of blackspot
seabream fisheries in the Alboran Sea; and (iv) a multiannual management plan
for turbot fisheries in the Black Sea.
On control and IUU activities: (v) the implementation of an international joint
inspection and surveillance scheme outside the waters under national
jurisdiction of the Strait of Sicily
to complement the multiannual plan adopted
in 2016; (vi) the implementation of a regional plan of action to combat IUU
fishing in the GFCM area of application.
On data collection: (vii) the submission of data on fishing activities in the
GFCM area of application; and (viii) the reporting of aquaculture data.
In addition, the GFCM adopted a set of resolutions, in particular a regional strategy for the
sustainable development of aquaculture in the Mediterranean and Black Seas, a network of
essential fish habitats and the creation of a permanent working group on vulnerable marine
ecosystems.
B. At EU level
Important steps were also taken at EU level to strengthen the implementation of the CFP in
the Mediterranean and Black Seas. This includes work on MAPs and discard plans,
improving the implementation of the Mediterranean Regulation in line with the objectives of
the CFP and strengthening enforcement and control. Member States have also launched some
encouraging initiatives to ensure sustainable fisheries also in these basins.
7
Malta MedFish4Ever Ministerial Declaration. Ministerial conference on the sustainability of
Mediterranean fisheries (Malta, 30 March 2017).
13
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Rollout of MAPs and discard plans
In the last year, the Commission has proposed two MAPs: one for small pelagic stocks in the
Adriatic Sea, which was adopted in February 2017
8
and is currently being discussed with the
co-legislators; and one for the fisheries exploiting demersal stocks in the western
Mediterranean Sea
9
, which was adopted in March 2018. The Western Mediterranean plan sets
F
MSY
ranges and conservation reference points for the main demersal stocks,
i.e.
hake, red
mullet, deep-water rose shrimp, Norway lobster, giant red shrimp and blue and red shrimp. In
line with a broad stakeholder consultation, the proposal introduces a fishing effort regime at
EU level for all trawls exploiting the concerned stocks. It is also complemented with
technical conservation measures such as closure areas. As with previous plans, this proposal
introduces provisions for the implementation of the landing obligation and regionalisation.
On discard plans, in 2017 the Commission extended the discard plan for demersal fisheries in
the Mediterranean, in term of species, area and fishing gears. In addition, the
de minimis
exemption to the landing obligation for certain small pelagic fisheries in the Mediterranean
has been renewed.
Improving the implementation of the Mediterranean Regulation
On the implementation of the Mediterranean Regulation, our focus is to align the national
management plans adopted under this Regulation
10
with the last CFP. In 2017, five national
management plans were reviewed by STECF and aligned to the extent possible with the CFP.
These include plans for fisheries conducted with boat seines, shore seines, gangui and small
purse seines in Croatia, France, Greece and Spain. This process will accelerate in 2018,
where we expect another 20 plans to be updated for the fisheries conducted by trawls and
purse seiners.
Strengthening enforcement and control
Given the importance of control and inspection activities in the Mediterranean and in
particular for the fisheries subject to multi-annual plans, Commission implementing Decision
2014/156/EU establishing a specific control and inspection programme (SCIP) has been
amended and enlarged to incorporate the fishery exploiting hake and deep-water rose shrimp
in the Strait of Sicily
11
.
8
COM(2017)097. Proposal for a Regulation of the European Parliament and of the Council establishing a multi-
annual plan for small pelagic stocks in the Adriatic Sea and the fisheries exploiting those stocks.
9
COM(2018) 115 final. Proposal for a Regulation of the European Parliament and of the Council establishing a
multi-annual plan for the fisheries exploiting demersal stocks in the western Mediterranean Sea
10
Council Regulation (EC) No 1967/2006 of 21 December 2006 (OJ L 36, 8.2.2007, p. 6).
11
Commission Implementing Decision (EU) 2018/17 of 5 January 2018 amending Implementing Decision
2014/156/EU establishing a specific control and inspection programme for fisheries exploiting stocks of bluefin
tuna in the Eastern Atlantic and the Mediterranean, swordfish in the Mediterranean and for fisheries exploiting
stocks of sardine and anchovy in the Northern Adriatic Sea (notified under document C(2017) 8687) (OJ L 4,
9.1.2018, p. 20).
14
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In addition, joint campaigns coordinated by the European Fisheries Control Agency have
been stepped up in 2017 (from 482 inspections in 2014
dedicated to bluefin tuna
to
2,855 inspections in 2017
–dedicated
to bluefin tuna, swordfish, albacore, small pelagics in
the Adriatic Sea and demersal species in the Strait of Sicily)
12
.
Member States initiatives
With the support of the Commission, Member States have adopted transitional management
measures at national level. For example, the French and Spanish national administrations, in
close coordination with stakeholders, agreed on common spatial measures for the
conservation of hake in the Gulf of Lion last November 2017.
12
EFCA activities in the Mediterranean and Black Seas (direct link here).
15
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III. Report on the balance between fishing capacity and fishing opportunities
In line with Article 22(4) of Regulation 1380/2013 (the CFP Regulation), the
Commission must report annually to the European Parliament and to the Council on
the balance between fishing capacity and fishing opportunities, taking into account the
assessment by the STECF.
This report covers the year 2016. It assesses the annual capacity of all the EU fleet
segments
based on the information included in the Member States’ reports submitted
to the Commission in 2017
13
. These reports must follow the common guidelines
adopted by the Commission in 2014
14
and, for the fleet segments for which structural
overcapacity has been identified, they must contain an action plan. The action plan
must set out the adjustment targets, tools and a clear time-frame for its
implementation.
The submission of the annual fleet reports is an ex-ante conditionality under European
Maritime Fisheries Fund (EMFF)
15
. Not submitting the annual fleet report and /or
failing to implement the action plan could result in a proportionate suspension or
interruption of relevant EU financial assistance to the Member States for the fleet
segments concerned as provided by the EMFF Regulation.
1. Member States' annual reports and action plans
All 23 coastal Member States submitted their reports to the Commission for 2016, 13
of which include an action plan
16
. The Commission requested STECF to:
tassess balance indicators for all EU Member States fleet segments;
review national reports on Member States efforts to achieve balance
between fleet capacity and fishing opportunities; and
assess action plans submitted for fleet segments where Member States
identified structural overcapacity.
The data used to compile the various indicators were collected under the Data
Collection Framework (DCF)
17
. All balance indicators provided and used in the
13
Article 22(2) Regulation (EU) No 1380/2013 of the European Parliament and of the Council of 11 December
2013 on the Common Fisheries Policy, amending Council Regulations (EC) No 1954/2003 and (EC) No
1224/2009 and repealing Council Regulations (EC) No 2371/2002 and (EC) No 639/2004 and Council Decision
2004/585/EC, OJ L 354, 28.12.2013, p. 22.
14
Guidelines for the analysis of the balance between fishing capacity and fishing opportunities according to Art
22 of Regulation (EU) No 1380/2013 of the European Parliament and the Council on the Common Fisheries
Policy, COM(2014) 545 final.
15
See Annex IV of Regulation (EU) No 508/2014 on the European Maritime and Fisheries Fund and repealing
Council Regulations (EC) No 2328/2003, (EC) No 861/2006, (EC) No 1198/2006 and (EC) No 791/2007 and
Regulation (EU) No 1255/2011 of the European Parliament and of the Council, OJ L 149, 20.05.2014, p. 1.
16
Three (Bulgaria, Croatia and Romania) Member States made amendments to the previous year’s action plan
and ten (France, Germany, Greece, Italy, Malta, Poland, Portugal, Slovenia, Spain and the UK) provided new
action plans.
17
Regulation (EU) 2017/1004 of European Parliament and the Council on the establishment of a Union
framework for the collection, management and use of data in the fisheries sector and support for scientific
16
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STECF Expert Working Group (EWG) 16-09 were calculated in accordance with the
2014 Commission Guidelines, which provide a common approach for estimating the
balance over time between fishing capacity and fishing opportunities. Regarding the
coverage of the data, the STECF concluded that, overall, there has been an
improvement in the data quality and coverage compared to previous years despite
some discrepancies.
Concerning the fleet segment coverage, the STECF noted that some of the indicators
could not be calculated for all fleet segments. This is either due to lack of data or, in
the case of economic and technical indicators, due to clustering of segments (done to
protect commercial confidentiality). Data deficiencies led to difficulties in the
calculation of balance indicators for fleet segments, making them unreliable or non-
representative. In some cases, only landings in weight were provided without the
corresponding landed values for all active fleet segments reported by a Member State.
The STECF analysis also confirmed a significant number of inactive vessels,
especially in the fleet segments with vessels under 10 m (small-scale costal fleets),
where many vessels are only used part-time and fishing is often not the only source of
income.
Since the entry into force of new CFP, 20 Member States
18
have identified, using
biological, economic or technical indicators and/or supplementary information, fleet
segments with fishing capacity not effectively balanced with fishing opportunities, or
showing latent signs of being imbalanced. Only three Member States concluded that
no fleet segments clearly demonstrated imbalance and did not submit action plans
19
.
advice regarding the common fisheries policy and repealing Council Regulation (EC) No 199/2008, OJ 157,
20.06.2017, p. 1.
18
Belgium, Bulgaria, Croatia, Cyprus, Denmark, France, Germany, Greece Ireland, Italy, Latvia, Lithuania,
Malta, Poland, Portugal, Romania, Slovenia, Spain, Sweden and United Kingdom.
19
Estonia, Finland and Netherlands.
17
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1908349_0019.png
Active fleet segments out of balance
Member
States
Total
number
of active
fleet
segment
Number of
fleet
segments
assesssed
Number of
fleet segment
out of
balance
Percentage of fleet
segment assessed
out of balance (%)
Area 27
Atlantic
Northeasat
Area 37
Mediterrea
n and
Blach Sea
BE
BG
HR
CY*
DK
EE
FI
FR
DE
GR*
IR
IT
LV
LT
MT
NL
PL
PT
RO
SI
ES
SE
UK
Tot
8
23
34
6
19
7
9
99
21
15
32
35
3
10
20
28
19
55
6
13
90
29
44
625
3
16
12
0
15
5
4
29
9
0
13
16
1
3
5
14
2
6
2
1
29
23
19
227
3
16
12
0
12
2
1
16
9
0
6
15
1
1
4
14
2
5
2
1
21
10
12
165
100
100
100
0
80
40
25
55.2
100
0
46
94
100
33.3
80
100
100
83.3
100
100
72.4
43.5
63
3
0
0
0
12
2
1
9
9
0
6
0
1
1
0
14
2
2
0
0
9
10
12
93
0
16
12
0
0
0
0
7
0
0
0
15
0
0
4
0
0
0
2
1
8
0
0
65
*
No fleet segment was assessed, either due to the lack of data or because the available data are not considered
representative.
To address situations of imbalance, Member States proposed a variety of management
tools in their action plans including:
-
fleet measures
(ban of new vessels, fleet conversion, reduction of the fishing
capacity, permanent or temporary cessation of activities and modernisation of
fishing fleet);
-
technical measures
(monitoring of landings, more selectivity or energy-
efficient gear, permitting schemes for certain fisheries, space and time-related
fishing restrictions);
-
economic measures
(support for development of marketing initiatives or
assistance to improve competitiveness); and
-
other measures,
such as measures to improve the cost-effectiveness of fishing
vessels and safety at work on board; monitoring of landing through weighing
18
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1908349_0020.png
of fishery products on automatic weighing and labelling machines; fishery
inspection measures; real time closures; support measures in the EMFF
Operational Programme (assistance for small-scale fleet vessels to meet
requirements of the landing obligation, transposition of the legal requirements
of the new CFP to promote a positive investment climate within the fishing
industry, reduction of fleet activity
20
).
Support for the permanent cessation of fishing activities through the scrapping of
vessels was eligible for funding under the EMFF until 31 December 2017 only for the
fleet segments considered not in balance. In 2016, Member States used permanent
cessation measures to decommission vessels from their fleet and reduce capacity.
According to the annual implementation reports for 2016, 147 fishing vessels were
decommissioned with public support, with a total public expenditure (certified
payment) of almost EUR 342 million, of which EUR 171 million came from the
EMFF.
20
See STECF-17-18, p.109-134.
19
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1908349_0021.png
2. T
HE
O
VERALL
C
APACITY OF THE
EU F
ISHING
F
LEET
As of December 2017, 82.912 vessels were registered in the EU fleet register with an
overall capacity of 1.487,983 in gross tonnage (GT) and 5.763,933 in kilowatts (KW).
This shows a reduction in 2017 of 1.45% in number of vessels, 6,54% in KW and
9.59% in GT. The fishing capacity of the EU fleet was 19,51 % below the capacity
ceilings for tonnage and 13,14 % below the power ceilings. Scrapping has contributed
to these results.
The Commission attaches great importance to the accuracy of the information
recorded in the EU fleet register. To this end, on 6 February 2017, it adopted a new
regulation on the Union fishing fleet register
21
. This regulation introduces a new
procedure that guarantees the update of the EU fleet register in real time. It gives the
Commission the possibility to check the correctness and correspondence between the
data submitted by Member State for any event and the data included in the snapshots.
Compliance with capacity ceilings on
December 2017
Effective capacity as percentage of capacity ceiling by Member State
100,00%
90,00%
80,00%
70,00%
60,00%
50,00%
40,00%
30,00%
20,00%
10,00%
0,00%
BE
BG
CY
DE
DK
ES
EE
FI
FR
EL
HR
IR
IT
LT
LV
ML
NL
PO
PR
RO
SI
SE
UK
TOT
GT
KW
21
Commission Implementing Regulation (EU) 2017/2018 of 6 February 2017 on the Union fishing fleet
register, OJ, L 34, 9.5.2017, p.9.
20
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1908349_0022.png
3. R
EGIONAL
A
SSESSMENT
In the North East Atlantic, the fishing capacity continues to decrease both in GT and
KW. However, according to the STECF
22
, there are fleet segments which are not in
balance with their fishing opportunities. According to Stock Harvest Indicator, in this
area, out of 625 fleet segments active in 2015, 93 were out of balance. The inactive
vessel and use indicators show a decreasing trend for most of fleet segments.
In the Mediterranean and Black Sea, a large number of fleet segments may not be in
balance with their fishing opportunities. These fleet segments rely on different stocks,
among which turbot, red mullet, Mediterranean horse mackerel, anchovy, pilchard,
common sole and swordfish. According to the STECF analysis, the inactive vessel
indicator shows a decreasing trend. By contrast, the vessel use indicator shows an
increasing trend.
Finally, the fleet in the outermost regions (OR) is composed of 4.164 fishing vessels,
which represents 5% of the total EU fleet. The fishing fleets in the outermost regions
are primarily composed by small-scale vessels targeting inshore and offshore
resources. Fleets in the outermost regions are also below their respective capacity
ceilings. In the period between January 2014 and December 2017, fleet capacities in
the outermost regions decreased in total by 3.9 % in GT and KW. STECF noted that
some fleet segments were out of balance and rely on overfished stocks. Because of
lack of data, it was not possible to assess the balance or imbalance of all fleet
segments. The ratio between current revenue and break-even revenue and for vessel
use indicator shows an increasing trend.
Total vessels in OR in Dec 2017
774
2.200
1.190
France
Portugal
Spain
22
See STECF-17-08, table 4.7.1 p.105 and tables from 7.1.1 and 7.1.4 p. 151 and 158.
21
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1908349_0023.png
Total GT in OR in Dec 2017
22.622
27.050
France
14.068
Portugal
Spain
Total KW in OR in Dec 2017
51.461
70.703
309.329
France
Portugal
Spain
22
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1908349_0024.png
4. C
ONCLUSIONS
The capacity of the EU fleet continued to decrease, following the same trend as in
previous years. Between December 2016 and December 2017, the EU fleet decreased
by 1.45% in number of vessels, by 6.54% in kilowatts (KW) and by 9.59% in gross
tonnage (GT).
In 2017, all 23 coastal Member States complied with their obligation to report
information on the capacity of their fleet segments.
13 of the Member States’ reports
included an action plan. Action plans contain a large variety of measures to address
overcapacity. These masures range from fleet measures, such as temporary or
permanent cessation, to technical, economic and control measures.
For the fleet segments that are not in balance, EMFF support for the permanent
cessation of fishing activities through the scrapping of vessels was eligible until 31
December 2017. Partly due to permanent cessation measures, in December 2017, the
fishing capacity of the EU fleet was 19,51 % below the capacity ceilings for tonnage
and 13,14 % below the power ceilings. This is expected to have a positive effect on the
conservation of marine biological resources.
Evolution of KW capacity between
Dec 2016 and Dec 2017
8.000.000
6.000.000
Axis Title
4.000.000
2.000.000
0
-2.000.000
Dec-16
KW
Series1
6.375.340
Dec-17
KW
5.763.933
Δ
6-2017
Δ
N(%)
-9,59%
23
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1908349_0025.png
Evolution of GT capacity between Dec 2016 and
Dec 2017
8.000.000
6.000.000
4.000.000
2.000.000
0
-2.000.000
Axis Title
Dec-16
GT
1.592.057
Dec-17
GT
1.487.983
Δ
6-2017
Δ
N(%)
-6,54%
Series1
Evolution in number of vessels betveen Dec
2016 and Dec 2017
2.000.000
Axis Title
0
Dec-16
-2.000.000
N
Dec-17
N
N
Dec-17
82.912
Δ
6-2017
Δ
N(%)
Δ
N(%)
Δ
6-2017
-1,45%
Series1
N
Dec-16
84.134
24
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1908349_0026.png
Table 1: decrease of the EU fishing Fleet capacity per Member State
Evolution of the fleet between 2008-17
0%
-2%
-4%
-6%
-8%
-10%
-12%
-14%
-16%
-18%
-20%
Figure 1: Reduction of the EU fishing fleet between 2008 and 2017 by number of vessels (N), power (KW)
and gross tonnage (GT)
Δ
N (%)
Δ
KW (%)
Δ
GT (%)
25
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1908349_0027.png
25
Coastal MS
24
GT
2.000.000
1.900.000
23
1.800.000
22
1.700.000
21
1.600.000
20
2008
2009
2010
2011
2012
2013
2014
2015
2016
2017
1.500.000
Figure 2: correlation between number of costal Member States and EU fishing Fleet gross tonnage (GT)
26
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1908349_0028.png
IV. Economic performance of the EU fishing fleet
The 2017 Annual Economic Report (AER) on the EU fishing fleet
23
provides a
comprehensive overview of the latest information available on the structure and economic
performance of the 23 coastal EU Member State fishing fleets. The results indicate that the
profitability of the EU fleet improved further in 2015, compared to 2014. This improvement
is expected to have continued into 2016 mainly as a result of increased landings and low fuel
prices. Forecasts for 2017 suggest that developments are offset by higher fuel prices
compared to 2016.
Direct employment generated by the sector amounted to 152,700 fishers, corresponding to
114,863 FTEs. Average annual wage per FTE was estimated at EUR 24.8 thousand, ranging
from EUR 1.4 thousand for Cypriot fishers to €UR 75 thousand for Belgian fishers.
The EU
fleet spent almost 4.8 million days at sea and consumed 2.3 billion litres of fuel. According to
the DCF data, the EU fleet landed 5 million tonnes of seafood in 2015 with a reported landed
value of EUR 7 billion.
The amount of Gross Value Added (GVA) and gross profit (all excl. subsidies) generated by
the EU fishing fleet (excl. Greece) in 2015 was EUR 3.9 billion and EUR 1.6 billion,
respectively. GVA as a proportion of revenue was estimated at 54%, up from 52% in 2014
and gross profit margin at 23%, up from 22% in 2014. With a total net profit of EUR 798
million, 11% of the revenue generated by the EU fleet in 2015 was retained as net profit.
23
JRC107883; 19-23 June 2017, Italy -- The 2017 Annual Economic Report on the EU Fishing Fleet - (EWG
17-01 and EWG 17-06). (pub:2017.08).
27
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1908349_0029.png
Figure 1: Increase in fleet profits since 2008
Results however varied by fishing region, as discussed below:
The overall performance of fleets operating in the
North Sea & Eastern Arctic region
was positive in 2015, and improved further compared to previous years. Overall, fleets
operating in the region spent almost 485 thousand days at sea in 2015, and landed 1.66
million tonnes of seafood valued at EUR 1.8 billion. The most profitable fleets were the
large (over 40 m) pelagic trawlers, with average gross profits estimated at around EUR
30,000 per day at sea. Factors that may have contributed to the positive situation include:
(1) recovery of several stocks, such as the North Sea common sole, plaice, herring,
haddock, saithe and cod; (2) increased TACs for a number of species such as plaice, hake,
cod, nephrops, sandeels and sprat; (3) higher average prices for a number of important
species, such as sole, plaice, common shrimp, cod and nephrops and (4) low fuel prices
resulting in lower energy costs. On the other hand, factors that may have hampered
economic performance in the region include reduced TACs and quotas for certain key
stocks, such as Atlantic mackerel.
Figure 2 : Revenue and profits trends for Member States fleets in the North Sea & Eastern Arctic
region
Overall, the EU
Baltic Sea
fleet spent almost 426 thousand days at sea in 2015, to land
approximately 613 thousand tonnes of seafood valued at EUR 217 million. A slight
increase in revenue (3%), combined with significant reductions in operating costs (e.g. -
28
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1908349_0030.png
17% in fuel costs), helped the overall situation of the Baltic Sea fleet move from a loss-
making position in 2014 to post a modest net profit in 2015. The main factors that may
have contributed to the positive situation, include: (1) decreasing fuel prices resulting in
lower energy costs; (2) policy management instruments in quota allocation and ITQs (as
introduced in some countries); (3) several pelagic fisheries that are exploited at F
MSY
and
thus at sustainable levels; (4) vessel decommissioning schemes (these measures positively
influenced Polish and Latvian fleet profitability) and (5) EMFF support, such as measures
aimed at increasing the added value of products (prioritised for Small Scale and Coastal
Fleets) and by-catch from landing obligations (for large-scale fleet). Conversely, factors
that may have negatively influenced the performance, include: (1) lower average prices
for several commercially important species, such as sprat, herring and cod; (2) reduced
TACs and quotas for Baltic cod, which has decreased consistently since 2014; (3) limited
fishing activity, especially for the SSCF which is highly dependent on weather conditions
and even in the favourable economic conditions could be the limiting factor for fleet
performance and (4) the long service life of the vessels, obsolete equipment and
insufficient investments increase the maintenance costs and may therefore reduce the fleet
profitability.
Figure 3: Trends on gross value added and
gross profit for Member States fleets
operating
in
the
Baltic
The major players in the
North East Atlantic
are the Spanish, French, British,
Portuguese and Irish fleets. The most important species include mackerel, horse mackerel,
hake and Norway lobster. Fleets operating in this region spent an estimated 1.5 million
days at sea and landed 1.4 million tonnes of seafood valued at EUR 2.4 billion. Despite
the decrease in landings, overall performance improved, with the majority of Member
State fleets generating net profits in 2015. In 2015, fuel price decreased and remained low
in 2016, while most fish prices remained stable or increased (including plaice and
common shrimp). Therefore, it is expected that economic performance further improved
as revenues are likely to have increased while costs decreased. Factors that may have
contributed to the positive situation include: (1) recovery of some stocks, such as herring
and Northern hake; (2) low fuel prices resulting in lower energy costs, especially for
pelagic fisheries; (3) increased TACs for Northern hake, herring and anglerfish; (4) stable
or higher average prices for some species, such as common sole and Nephrops have
helped maintain profitability and (6) capacity reduction (with or without public support)
leading to decreased fixed costs. Factors that may have hampered economic performance
29
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1908349_0031.png
in the region include: (1) reduced quotas for mackerel, common sole, plaice and cod; (2)
lower average prices and total landings for commercially important species, such as,
plaice, common shrimp, herring and mackerel.
Figure 4: Trends on landings in weight and value from Member States fleets
operating in the NE Atlantic fishing region
24
Figure 5: Trends on gross profit for Member States fleets operating in the NE Atlantic
region
24
Data source: Member States data submissions under the DCF 2017 Fleet Economic (MARE/A3/AC(2017));
All monetary values have been adjusted for inflation; constant prices (2015).
30
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1908349_0032.png
Figure 6: Trends on net profit for Member States fleets operating in the NE Atlantic
region
Overall, the economic situation of EU fleets operating in the
Mediterranean & Black
Sea
improved: 2015 was the best year so far analysed, in particular for the Italian fleet,
which is the main player and contributor to trends in the region. The main species include
anchovy, sardine, and hake. Overall, fleets operating in the region spent almost 2.1
million days at sea in 2015, and landed 368 thousand tonnes of seafood valued at EIR 1.3
billion. Factors that may have contributed to improved economic performance in the
region include: (1) higher revenues brought on by increased landings and higher average
prices; (2) low fuel prices, which reduce energy costs; (3) more fisheries where stocks are
being exploited at rates consistent with achieving F
MSY
and fleets are showing positive
trends, particularly in landings (e.g. deep sea rose shrimp in North Tyrrhenian-Ligurian
Sea). Other factors that affected fleet performance in this region include: (1) overfishing
and stock status - only very few demersal stocks are currently being exploited at rates
consistent with achieving F
MSY
; (2) marine resources and ecosystems under increased
pressure, driven by diversification and intensification of marine and maritime activities;
(3) high competition between professional fishers and recreational fishers; (4) new
management measures, in particular the introduction of a TAC for swordfish and for
pelagic fisheries in the Adriatic Sea - fishers are concerned that these TACs will have a
negative impact on their profits in the future; (5) introduction of two Fisheries Restricted
Areas (RFAs) in the Strait of Sicily and (6) lack of investments in fishing gears with
lower environmental impact and greater energy efficiency (energy efficiency has not
improved in the region in the recent years).
31
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1908349_0033.png
Figure 7: Revenue and profits trends for Member States fleets operating in the Mediterranean &
Black Sea
25
Preliminary results for 2016 indicate a 69 % increase in net profits compared wih 2015,
registering record high profits of EUR 1,3 billion for the EU fleets. Results suggest that the
EU fleet as a whole was profitable in 2016, with an estimated net profit margin of 17%.
Gains in 2016 are offset slightly in 2017 and 2018 due to the increase in fuel costs, however
the EU fleet remains profitable with an average net profit margin above 15%. It should be
noted that EU fleet moved from marginal profits in 2009 (32 millions) to register 1,3 billion
of net profis in 2016. Similarly, gross value added and revenue increased significnatly over
the period 2009-2016.
The active EU small-scale coastal fleet (SSCF) employes 77,708 fishers or 47,789 in FTE
(including Greece). In 2016, the number of small-scale coastal vessels increased (+7%)
mainly due to a significant increase in licenced Croatian SSCF vessels, while FTE increased
by only 2.5%. As a whole, the EU SSCF was profitable in 2015: lower energy and capital
costs in 2015 together with higher revenues fostered a 6.5% increase in GVA, 28% increase
in gross profit and 98.4% increase in net profit compared to 2014. Net profit increased from
EUR 46.4 million in 2014 to EUR 92.1 million in 2015 (excluding Greece). Projection
results suggest that fishing effort, in days at sea, decreased 2.3% in 2016. The reduction in
fishing effort combined with low fuel prices, indicate that energy costs decreased by 22%.
Landed weight remained stable at around 284 thousand tonnes while landed value, estimated
at EUR 851 million in 2016, increased 2.6%. These preliminary findings suggest that the EU
SSCF generated EUR 650 million in GVA, an increase of 5.4% compared to 2015. Labour
productivity (GVA per FTE) also increased, from EUR 21.4 thousand in 2015 to EUR 22
thousand in 2016. Gross profit was estimated at EUR 236.7 million, a 10.8% increase on
2015. Positive economic developments can also be seen in the performance indicators - GVA
to revenue estimated at 67% (+3%%) and gross profit margin estimated at 24.4% (+8.2%) in
2016. With increased capital costs, net profit was estimated at EUR 72.3 million, a decrease
of 21.6% compared to 2015, year with the highest net profit (EUR 92 million) observed over
the period analysed (2008-2015). Net profit margin moves from 10.1% in 2015 to 7.7% in
25
Data source: Member State data submissions under the DCF 2017 Fleet Economic (MARE/A3/AC(2017)).
32
kom (2018) 0452 - Ingen titel
2016. However, the 2016 gains are offset slightly in 2017 with fuel costs increasing 10.3%.
The SSCF remains profitable with gross and net profit margins of 23% and 7.1%,
respectively.
While the EU SSCF as a whole was profitable over the time period analysed, results at the
regional and Member State level are mixed. At the regional level, results suggest that the
North Sea, Northeast Atlantic, Mediterranean & Black Sea and Outermost region SSCFs
were profitable in 2015, generating 2.8%, 8.4%, 6.6% and 8% net profit margins respectively.
Conversely, the SSCFs operating in the Baltic Sea suffered net losses, amounting to
EUR 18.37 million in 2015. The Danish, Finnish, Polish and Swedish Baltic SSCFs were the
most unprofitable, collectively suffering over EUR 19 million in net losses in 2015.
33
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1908349_0035.png
Figure 8: Main indicators for the EU small-scale coastal fleet 2008-2015 and projections for 2016 and 2017
34
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1908349_0036.png
V. The implementation of the Landing Obligation
1. Progress Report
For years fishers have adopted uncontrolled discarding practices, returning unwanted catches
to the sea, dead or alive. The 2014 reform of the CFP aims to gradually eliminate this
wasteful practice of discarding. For this purpose, Article 15 of the CFP Regulation introduced
the obligation to retain and land all catches of species subject to catch limits and in the
Mediterranean also under minimum sizes, caught both in EU waters or by Union fishing
vessels outside EU waters, except in waters under the national jurisdiction of a third country.
The CFP provides for the progressive phasing-in of the landing obligation, with full
implementation as of the 1 January 2019.
Figure 1: Percentage of TACs partially or fully subject to the LO by sea basin and year*
* DP: Discard plans; JR: Joint Recommendations
By 2016, the proportion of EU landings value under the landing obligation (LO) was
estimated to be 21%. The Member States with the highest proportion of landings (excluding
pelagics) under the landing obligation were Belgium (61%), the Netherlands (43%), Sweden
(39%) and Denmark (38%). By 2019, when full implementation is planned with all EU quota
species and those with minimum conservation reference size (MCRS) in the Mediterranean
subject to the landing obligation, it is estimated that 40% of landed value will be under the
landing obligation. The Member States identified in 2016 still show the highest proportion in
landings under the landing obligation (Belgium, the Netherlands, Denmark & Sweden) and
are joined by France, the UK, Ireland, Greece and Slovenia; all with at least 40% of landings
under the landing obligation.
35
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1908349_0037.png
Table 1: Cumulative increase in dependence on species under LO (excluding pelagics)
Member State
Belgium
Bulgaria
Cyprus
Germany
Denmark
Spain
Estonia
Finland
France
UK
Greece
Croatia
Ireland
Italy
Lithuania
Lativia
Malta
Netherlands
Poland
Portugal
Romania
Slovenia
Sweden
Grand Total
Value (€)
81,894,230
2,393,024
6,076,738
122,209,222
243,002,674
771,947,670
3,807,057
8,438,019
959,036,329
753,189,858
102,344,168
29,966,958
149,258,776
730,485,586
3,974,335
4,313,157
6,053,717
268,498,596
24,041,154
187,939,450
4,005,922
1,091,636
65,359,031
4,529,327,309
Pelagics
17%
42%
46%
24%
9%
41%
23%
21%
37%
27%
33%
21%
18%
49%
9%
7%
38%
21%
11%
43%
87%
29%
10%
33%
others
83%
58%
54%
76%
91%
59%
77%
79%
63%
73%
67%
79%
82%
51%
91%
93%
62%
79%
89%
57%
13%
71%
90%
67%
2015
0%
0%
0%
1%
9%
0%
0%
2%
0%
0%
0%
0%
0%
0%
0%
0%
0%
0%
2%
0%
0%
0%
6%
1%
2016
61%
0%
0%
20%
38%
11%
0%
2%
27%
33%
0%
0%
32%
0%
0%
0%
0%
43%
2%
5%
0%
0%
39%
21%
2017
61%
0%
0%
25%
44%
11%
3%
4%
27%
33%
0%
0%
32%
0%
5%
15%
0%
43%
39%
5%
0%
0%
45%
22%
2018
61%
0%
0%
25%
44%
11%
3%
4%
27%
33%
0%
0%
32%
0%
5%
15%
0%
43%
39%
5%
0%
0%
45%
22%
2019
83%
22%
34%
39%
48%
27%
3%
4%
51%
46%
47%
28%
45%
33%
5%
15%
14%
53%
39%
23%
7%
57%
47%
40%
total no. total no.
% of segmentsof top 10*
%
fleet segments
segments >50% >50%
fleet segments
4
3
75%
75%
16
2
13%
20%
6
1
17%
17%
14
8
57%
60%
19
12
63%
70%
59
6
10%
30%
4
-
0%
0%
5
-
0%
0%
52
17
33%
70%
29
15
52%
50%
13
8
62%
60%
23
9
39%
50%
22
8
36%
40%
23
3
13%
0%
5
2
40%
40%
4
-
0%
0%
20
1
5%
10%
14
8
57%
60%
7
4
57%
57%
50
6
12%
10%
4
-
0%
0%
4
2
50%
50%
7
5
71%
71%
-
-
0%
0%
Based on the obligation to report on the implementation of the landing obligation in
Regulation (EU) No. 1380/2013, the Commission has obtained information from EU Member
States, Advisory Councils and other relevant sources on
26
:
the steps taken by Member States and the producer organisations to comply with the
landing obligation;
the steps taken by Member States regarding the control of compliance with the landing
obligation;
the socio-economic impact of the landing obligation;
the effect of the landing obligation on safety on board fishing vessels;
the use and outlets of catches below the minimum conservation reference size of a species
subject to the landing obligation;
port infrastructures and of vessels’ fitting with regard to the landing obligation, for each
fishery concerned; and
Source: "Evaluation
of Member State's Annual Reports on the Landing Obligation (for 2017)",
dated March
2018, DG MARE Contract No. ARES(2018)1564295.
26
36
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the difficulties encountered in implementing the landing obligation and recommendations
to address them.
In 2016, a STECF Expert Working Group developed a voluntary questionnaire to facilitate
Member States and Advisory Councils to report on the impact of the landing obligation and
on national steps taken to implement it. For the exercise covering 2017, the Commission
addressed two additional questions to Member States, focusing on enforcement of the landing
obligation at sea and reported infringements.
For 2017, the Commission has received reports from 15 Member States and 2 Advisory
Councils. As a consequence, care is required in interpreting year on year change since the
composition of respondents in the different areas has changed. It is also important to
recognise that changes reported in a questionnaire do not necessarily imply a successful
outcome related the landing obligation. Such an outcome will depend on confidence that there
has been significant change in fishing practice at sea and adequate monitoring and control of
all fishing operations to ensure that catches are fully accounted for. Moreover, it needs to take
into consideration that the quality of the reports received vary widely: the level of detail they
contain therein varies extensively, as many reports repeated information already included in
the previous reports.
Information on discard quantities presented by Member States is scant and, based on the
questionnaires, it is not possible to say whether there have been any changes in discard
quantities. Member States continue to indicate that difficulties encountered so far have been
minimal but several highlight that the most significant issue they face is the industries’
reluctance to implement the landing obligation despite considerable efforts to disseminate
information to them. They also report that fishermen seem slow to change behaviour and in
the Mediterranean, in some Member States in the Baltic and in the Black Sea, a “business
as
usual”
mentality seems to prevail.
There continues to be a wide divergence in the approach to promoting compliance with the
landing obligation. Member States have continued to make significant efforts into
disseminating information to fishermen and to engage with the relevant Advisory Councils
(for example in conducting choke species analysis - a generally more prominent activity in
2017). A number of Member States reported changes in 2017 to ensure compliance with the
landing obligation. Specific training and dedicated workshops for inspectors on control
elements of the landing obligation have continued with facilitation by EFCA. Some Member
States elaborated on their risk based approach to control and monitoring and some provided
data on last haul analysis. This approach seems to have bedded down well in some areas such
as the Baltic. New control tools such as remote electronic monitoring and CCTV continued
to be tested in 2017 by several countries although there is little evidence of them being used
on a mandatory basis. A number of the reports for 2017 raised the issue of ensuring a level
playing field before being prepared to commit to these new approaches.
A number of Member States have undertaken specific studies and pilot projects to test
selective gears or avoidance strategies and some have reported outcomes for 2017 and
strategies for increasing uptake of these gears. Fewer actions have been taken by Member
States in the Mediterranean and Black Sea where fewer difficulties with implementing the
landing obligation have been reported.
37
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Member States have continued to apply for various exemptions included under the regional
discard plans and a few have adjusted their national quota management systems. Inter-species
quota flexibility has mostly not been used but inter-annual flexibility mechanisms have.
Most Member States report that it remains difficult to assess the socio-economic impacts of
the landing obligation, indicating that problems have been minimal so far but could increase
as more species are included. For 2017 one Member State provided details of a completed
study which highlighted problems for some, but not all, sectors. During 2017, there was again
no clear evidence of the landing obligation causing safety issues on board fishing vessels and
reports from Member States were identical to the previous year.
Landings of fish below minimum conservation reference size (MCRS) reported for 2017 by
Member States are generally low across the different regions. The landed material below
MCRS has been used for fish meal, pet food or as bait for pot fisheries. One study of
alternative uses suggest that low prices, limited volume and variable composition of below
MCRS material makes the alternatives economically unattractive. The reports for 2017 saw an
increase in the extent to which EMFF funding to improve the infrastructure of ports as well as
modifications on board fishing vessels has been applied for. Specific actions so far include the
provision of cold storage facilities onshore and aboard vessels for storage of unwanted
catches.
Responses for 2017 continue to articulate the issues raised already last year (i.e. choke
species, confusion in interpretation of regulation). Of greatest concern is the uncertainty over
the reporting by fishermen of fish discarded under exemptions (i.e. de minimis and high
survivability), discards of fish currently not subject to the landing obligation and catches of
fish below MCRS. In part this has been due to the Electronic recording and reporting system
(ERS) not being adapted to make it possible to record such catches and, operational facilities
need to be fit for purpose to ensure information is correctly recorded.
Overall, it appears that the impacts of the landing obligation on Member States and the fishing
industry are low. However, the majority of Member States and the Advisory Councils indicate
these will increase with full implementation in 2019. While Member States and Advisory
Councils seem to be working more closely under regionalisation the reluctance of the fishing
industry to embrace change is a major concern. The lack of accurate reporting of fish
discarded under exemptions allowed for under the landing obligation, the very low volumes
of fish below MCRS being landed and the difficulties experienced by Member States in
monitoring such catches are major concerns and hint to compliance problems.
2. State of play of discard plans
In principle, details of the implementation of the landing obligation must be specified in a
multiannual plan (MAP). These include technical measures, the fixing of MCRS where
appropriate, high survivability exemptions, and
de minimis
exemptions of up to 5% of the
total annual catches. The two MAPs agreed under the new CFP so far, the Baltic MAP and the
North Sea MAP, contain indeed provisions on the implementation of the landing obligation
and introduce regionalisation as a way to shape delegated acts establishing discard plans for
38
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1908349_0040.png
these sea basins. The first delegated Regulation on the implementation of the landing
obligation under a MAP, the Baltic MAP, entered into force earlier this year
27
.
In the absence of MAP, the European Parliament and the Council (the co-legislators) initially
empowered the Commission to adopt discard plans through delegated acts on a temporary
basis and for a period of no more than three years. However, due to delays in the preparation
and adoption of MAPs, the initial three year period was proved to be too short: several discard
plans were expiring at the end of 2017, with no MAP to rule the details of the implementation
of the landing obligation. Practically, this meant that the flexibilities referred to in Article 15
CFP, in particular the possibility to introduce exemptions would be lost for the sea basins for
which no MAP was in place.
To tackle this issue the Commission rapidly prepared a proposal to amend Article 15(6) of the
CFP Regulation and extend the possibility to adopt discard plans for an additional period of 3
years, in the absence of a MAP. This proposal was agreed by the colegislators
28
and all the
discard plans expiring at the end of 2017 were renewed in time.
The full list of discard plans adopted under Article 15(6) CFP currently in force follows
(chronological order of adoption):
1.
Commission Delegated Regulation (EU) 2015/2438 of 12 October
2015 establishing a discard plan for certain demersal fisheries in
north-western waters
Commission Delegated Regulation (EU) 2015/2439 of 12 October
2015 establishing a discard plan for certain demersal fisheries in
south-western waters
Commission Delegated Regulation (EU) 2015/2440 of 22 October
2015 establishing a discard plan for certain demersal fisheries in the
North Sea and in Union waters of ICES Division IIa
Commission Delegated Regulation (EU) 2016/2250 of 4 October
2016 establishing a discard plan for certain demersal fisheries in the
North Sea and in Union waters of ICES Division IIa
Commission Delegated Regulation (EU) 2016/2374 of 12 October
2016 establishing a discard plan for certain demersal fisheries in
South-Western waters
Commission Delegated Regulation (EU) 2016/2375 of 12 October
2016 establishing a discard plan for certain demersal fisheries in
North-Western waters
Commission Delegated Regulation (EU) 2016/2376 of 13 October
2016 establishing a discard plan for
mollusc bivalve Venus spp. in
the Italian territorial waters
Commission Delegated Regulation (EU) 2016/2377 of 14 October
2016 amending Delegated Regulation (EU) No 1394/2014
establishing a discard plan for certain pelagic fisheries in
South-
2.
3.
4.
5.
6.
7.
8.
27
Commission Delegated Regulation (EU) 2018/306 of 18 December 2017 laying down specifications for the
implementation of the landing obligation as regards cod and plaice in Baltic Sea fisheries (OJ L 60, 2.3.2018,
p. 1).
28
Regulation (EU) 2017/2092 of the European Parliament and of the Council of 15 November 2017 amending
Regulation (EU) No 1380/2013 on the common fisheries policy, (OJ L 302, p. 1).
39
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1908349_0041.png
9.
10.
11.
12.
13.
14.
15.
16.
17.
18.
19.
Western waters
Commission Delegated Regulation (EU) 2017/86 of 20 October 2016
establishing a discard plan for certain demersal fisheries in the
Mediterranean Sea
Commission Delegated Regulation EU) 2017/87 of 20 October 2016
establishing a discard plan for turbot fisheries in the
Black Sea
Commission Delegated Regulation (EU) 2017/2167 of 5 July 2017
amending Delegated Regulation (EU) 2016/2374 establishing a
discard plan for certain demersal fisheries in
South-Western waters
Commission Delegated Regulation (EU) 2018/45 of 20 October 2017
establishing a discard plan for certain demersal fisheries in the
North
Sea and in Union waters of ICES Division IIa
for the year 2018
Commission Delegated Regulation (EU) 2018/44 of 20 October 2017
amending Delegated Regulation (EU) 2016/2374 establishing a
discard plan for certain demersal fisheries in
South-Western waters
Commission Delegated Regulation (EU) 2018/46 of 20 October 2017
establishing a discard plan for certain demersal and deep sea fisheries
in
North-Western waters
for the year 2018
Commission Delegated Regulation (EU) 2018/153 of 23 October
2017 amending Delegated Regulation (EU) 2017/86 establishing a
discard plan for certain demersal fisheries in the
Mediterranean Sea
Commission Delegated Regulation (EU) 2018/211 of 21 November
2017 establishing a discard plan as regards salmon in the
Baltic Sea
Commission Delegated Regulation (EU) 2018/188 of 21 November
2017 amending Delegated Regulation (EU) No 1394/2014
establishing a discard plan for certain pelagic fisheries in
South-
Western waters
Commission Delegated Regulation (EU) 2018/189 of 23 November
2017 amending Delegated Regulation (EU) No 1395/2014
establishing a discard plan for certain small pelagic fisheries and
fisheries for industrial purposes in the
North Sea
Commission Delegated Regulation (EU) 2018/190 of 24 November
2017 amending Delegated Regulation (EU) No 1393/2014
establishing a discard plan for certain pelagic fisheries in
North-
Western waters.
3. Use of the EMFF for measures linked to the implementation of the landing
obligation
The prohibition to discard is a radical change in the management of the fishing activity.
Therefore several measures are eligible for funding under the European Maritime and
Fisheries Fund (EMFF) to facilitate the implementation of the landing obligation. The
Commission commissioned a study to assess the use of the EMFF to support the landing
obligation
29
.
"FAME
Support Unit, AT01.2 ad-hoc consultancy Landing Obligation Final Report (AT1.2 5/5)",
Version 1,
Febriuary 2018.
29
40
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1908349_0042.png
According to this study, to date, an overall amount of EUR 49 million in EMFF funding is
committed or planned to support the implementation of the landing obligation, i.e. less than
1% of the total funds allocated to sustainable fisheries under Union Priority 1:
Promoting
environmentally sustainable, resource-efficient, innovative, competitive and knowledge-based
fisheries (UP1).
Another EUR 59 million was spent under the previous funding instrument,
the EFF.
The main findings of the study are discussed below:
Four Member States (DK, IE, PT, UK) reported an uptake of measures to limit the impact of
fishing activities on the environment and to implement the landing obligation. Most projects
relate to the improvement of fishing gear selectivity and avoidance of protected species. Some
Member States also funded studies on the handling and valorisation of unwanted catches.
However, most Member States reported a delayed start of operations under UP1 in relation to
the need to finalise administrative and technical arrangements to manage applications and
projects. Nine Member States (BE, BG, CZ, FI, FR, HU, NL, RO, SK) could not start UP1
implementation for this reason.
Over the 2014-2016 period, DK and UK appear to be the two Member States having
committed significant EMFF funding to the implementation of the LO. Measures include
support to vessel operators to reduce the impact of fishing on the environment, innovation,
use of unwanted catches, and port measures to facilitate compliance with the obligation to
land all catches.
3.1 Extent of EMFF support for the implementation of the landing obligation to date
Regarding the extent of EMFF support, a filtering exercise was undertaken with the Infosys
database
30
to identify projects that would be relevant for the implementation of the landing
obligation. This process identified an interesting distinction: some projects to reduce
‘unwanted catch’ are related to by-catch
of non-commercial species such as birds or seals.
Therefore, although at first they they appeared to be relevant for the landing obligation, they
are not directly supporting its implementation.
The analysis below is based on aggregated responses from Member States Managing
Authorities, who reviewed the filtered Infosys data (where some projects related to the
landing obligation had been identified) and provided an update. Based on this, the table below
comprises an overview of total EMFF share of support per Member States and the focus of
supported operations. The table is divided in two columns: the first column relates to
operations which wete carroed pit under the EMFF up to the end of 2016 and which are
considered to have contributed to the implementation of the landing obligation.
30
Commission Implementing Regulation (EU) No. 1242/2014 of 20 November 2014 laying down rules pursuant
to the EMFF Regulation with regard to the presentation of relevant cumulative data on operations and
Commission Implementing Regulation (EU) No. 1243/2014 of 20 November 2014 on the information to be sent
by Member States, as well as data needs and synergies between potential data sources.
41
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1908349_0043.png
Table 3: Overview of EFF and EMFF support per Member States
EFF
M e m be r
Sta te
Be l g i u m ( BE)
Bu l g a ri a ( BG)
Cro a t i a ( H R )
Cy p ru s ( CY)
D e n m a rk ( D K)
Es t o n i a ( EE)
Fi n l a n d ( FI )
Fra n ce ( FR )
Ge rm a n y ( D E)
Gre e ce ( EL)
I re l a n d ( I E)
I t a l y ( I T)
La t v i a ( LV)
Li t h u a n i a ( LT)
M a l t a ( M T)
N e t h e rl a n d s
( N L)
Po l a n d ( PL)
Po rt u g a l
( PT)
372 963
867 069
133 671 451
59 045 857
29 286
3 429 501
19 121 529
49 501 978
3 697 688
303 222
3 697 688
332 508
3 429 501
R o m a n i a ( R O)
Sl o v e n i a ( SL)
Sp a i n ( ES)
Sw e d e n ( SE)
Un it ed
Ki n g d o m ( U K)
t o t a l re ce i v e d
EFF m i n u s
I t aly
4 233 892
33 239 184
1 656 414
337 500
5 890 000
2 674 028
758 683
74 625 594
233 679
1 469 264
77 390
3 526 000
637 500
5 250 000
370 000
1 315 000
5 250 000
2 072 943
1 392 390
3 526 000
637 500
337 500
7 546 414
3 100 000
1 800 000
8 201 708
6 578 147
150 000
1 009 029
4 500 000
150 000
4 500 000
15 788 884
EM FF
to 2 0 1 6
122 000
Associa t e d spe n d
12 000 039
2017
105 500
P la n n e d
Tot a l
227 500
613 151
613 151
14 285 738
16 094 711
EMFF potential total end
2018:
49 501 978
By the end of 2017, around EUR 30 million of EMFF had been committed to projects related
to the landing obligation across ten Member States. Denmark has committed the most for LO-
related projects at EUR 14.7 million, accounting for around 49% of total EMFF support up to
2017. Out of around EUR 8.2 million EMFF support in Denmark up to 2016, about EUR 4
million was focused on gear selectivity, EUR 2 million for ports, EUR 1 million for
innovations.
By the end of 2016 the UK had committed EUR 3.4 million to port investments and the
Netherlands continued its significant funding support to LO implementation with EUR 1.7
million committed to vessel-based research and fleet investment.
In 2017, the level of commitment accelerated with EUR 16 million of EMFF support
committed (compared to EUR 14 million in total from 2014-2016), resulting from the
delayed start to EMFF programme implementation in most Member States as well as the
increased demand to help address the landing obligation as it was being phased in. In 2017,
EUR 6.6 million of EMFF funding supported additional fleet investments in Denmark and
EUR 3.7 million supported fleet investments in Spain. Ireland and Sweden also made
commitments to port investments.
Latvia committed EMFF funds to a major processing investment of EUR 3.5 million related
to the landing obligation. The projects involve fishermen’s groups and an NGO and aim to
increase added value and the use of unwanted catches related to the production of fish protein
and oil.
42
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3.2. Planned EMFF support for LO implementation
The table below shows an overview of Member States estimations of planned EMFF funding
related to the landing obligation. In total, a planned EUR 19 million of EMFF funds is
reported to be allocated to address the implementation of the landing obligation from 2018
onwards.
Table 4: Overview of planned EMFF support from 2018 onwards per Member State
EM FF
Me m be r Sta te
fr om 2 0 1 8
Focu s
Cyp ru s ( CY)
150 000
port investment
D en m ark ( D K)
1 009 029
fleet investment
Est o n ia ( EE)
4 500 000
processing investment
Greece ( EL)
5 250 000
3m innovation, 1,5m added
value, 0,75m port investment
I rel an d ( I E)
370 000
gear selectivity
I t aly ( I T)
1 315 000
fleet investment
Li t h u an ia ( LT)
637 500
port investment
2,6m gear investment, 2,5m
research, 1m handling
unwanted catch
N et h erlan d s ( N L)
5 890 000
To t al
19 121 529
*MS not listed report no planned LO-related commitments
Source: MA responses, FAME 2018
The Netherlands plans the biggest spend of EUR 5.9 million on gear investment, research and
handling unwanted catch. Greece, which has made no commitments to date, is planning
similar levels of support from 2018 onwards with EUR 3 million on innovation, EUR 1.5m on
value-added and EUR 0.75m on port investment. Denmark is continuing its significant fleet
investment with EUR 1.5m of support planned. Lithuania and Cyprus are planning some port
investment related to the landing obligation.
43
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Similar to Latvia in 2017, Estonia reports that it plans support of EUR 4.5 million for a
processing investment to a fishermen’s group under Article 68 (processing
for non-human
consumption).
3.3 EMFF operations completed
Not many EMFF operations related to the landing obligation have been completed as yet.
Most relevant projects are still ongoing. Notable exceptions are:
Project “Valduvis” in Belgium, concerning
traceability and certification;
“Fast Track –
Sustainable and cost-efficient solutions in fisheries under the landing
obligation” in Denmark; the project includes establishing a platform for cooperation in
order to identify, collect and distribute knowledge and best practice as well as cost
efficient trials of selective gear in order to ensure sustainable fisheries and improved
management under the LO;
Pilot project with scientific observers on board commercial bottom trawlers in
southwestern waters, testing different gears in order to increase knowledge on selectivity
and catch composition, including the use of video cameras attached to the net to know its
performance in the water while trawling but also the performance of fish caught into the
net;
Project “Added value, product quality and use of unwanted by-catch” in Lithuania.
44