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THE COMMISSION OF THE EUROPEAN COMMUNITIES,
Having regard to the Treaty establishing the European Community,
Having regard to Council Regulation (EC) No 199/2008 of 25 February 2008 concerning the establishment of a Community framework for the collection, management and use of data in the fisheries sector and support for scientific advice regarding the common fisheries policy(1), and in particular Articles 3(1) thereof,
Whereas:
(1) Regulation (EC) No 199/2008 establishes a Community framework for the collection, management and use of data for the purpose of forming a solid basis for scientific analyses of fisheries and of providing for the formulation of sound scientific advice for the implementation of the common fisheries policy (hereinafter referred to as the CFP).
(2) Member States should establish multiannual national programmes for the collection, management and use of data in accordance with the multiannual Community programme.
(3) It is therefore necessary to establish a multiannual Community programme covering the collection of information needed to support scientific analysis required in the framework of the CFP and the management and use of this information.
(4) The measures provided for in this Decision are in accordance with the opinion of the Management Committee for Fisheries and Aquaculture.
HAS DECIDED AS FOLLOWS:
The multiannual Community programme referred to in Article 3(1) of Regulation (EC) No 199/2008 is defined in the Annex.
Done at Brussels, 6 November 2008.
For the Commission
Joe Borg
Member of the Commission
:
vessels that have been engaged in any fishing operation (more than zero days) during a calendar year. A vessel that has not been engaged in fishing operations during a year is considered ‘inactive’.
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sampling all or a predefined assemblage of species, simultaneously in a vessel's catches or landings.
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any continuous period of 24 hours (or part thereof) during which a vessel is present within an area and absent from port.
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a group of vessels with the same length class (LOA) and predominant fishing gear during the year, according to the Appendix III. Vessels may have different fishing activities during the reference period, but might be classified in only one fleet segment.
:
each day is attributed to the area where the most fishing time was spent during the relevant day at sea. However, for passive gears, if no operation took place from the vessel during a day while at least one (passive) gear remained at sea, that day will be associated to the area where the last setting of a fishing gear was carried out on that fishing trip.
:
means any voyage by a fishing vessel from a land location to a landing place, excluding non-fishing trips (a trip by a fishing vessel from a location to a land location during which it does not engage in fishing activities and during which any gear on board is securely lashed and stowed and not available for immediate use).
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a group of fishing operations targeting a similar (assemblage of) species, using similar gear, during the same period of the year and/or within the same area and which are characterised by a similar exploitation pattern.
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all vessels in the Community Fishing Fleet Register as defined in Commission Regulation (EC) No 26/2004 of 30 December 2003 on the Community fishing fleet register(2).
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species of relevance for management purposes and for which a request is made by an international scientific body or a regional fisheries management organisation.
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time calculated from the point where each individual unit of gear has been set, to the time when the same unit starts to be removed.
The Community programme comprises of the following modules:
Module of evaluation of the fishing sector:
The data collection programme for the fishing sector contains the following sections:
Section for the collection of economic variables;
Section for the collection of biological variables;
Section for the collection of transversal variables;
Section for research surveys at sea.
Module of evaluation of the economic situation of the aquaculture and processing industry sectors:
Section for the collection of economic data for the aquaculture sector;
Section for the collection of economic data for the processing industry.
Module of evaluation of the effects of the fishing sector on the marine ecosystem.
Module for management and use of the data covered by the data collection framework.
:
level making it possible to estimate a parameter either with a precision of plus or minus 40 % for a 95 % confidence level or a coefficient of variation (CV) of 20 % used as an approximation;
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level making it possible to estimate a parameter either with a precision of plus or minus 25 % for a 95 % confidence level or a coefficient of variation (CV) of 12,5 % used as an approximation;
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level making it possible to estimate a parameter either with a precision of plus or minus 5 % for a 95 % confidence level or a coefficient of variation (CV) of 2,5 % used as an approximation.
‘vessels using Polyvalent active gears’ if it only uses active gears;
‘vessels using Polyvalent passive gears’ if it only uses passive gears;
‘vessels using active and passive gears’.
Clustering may be necessary in order to design the sampling plan and to report economic variables;
Member States shall report which fleet segments have been grouped at the national level and shall justify the clustering on the basis of statistical analysis;
In their annual report, Member States shall report the number of sampled vessels for each fleet segment regardless of any clustering made to collect or provide the data;
Regional coordination meetings shall define homogeneous clustering methodology at the level of supra regions so that economic variables are comparable.
the share of the various stocks in these landings for herring in the Skagerrak IIIA-N, Kattegat IIIa-S, and Eastern North Sea separately and salmon in the Baltic Sea;
the share of the various species for those group of species that are internationally assessed, e.g. megrims, anglerfishes and elasmobranches;
the strata defined at national level do not overlap the metiers defined in Appendix IV (1 to 5);
the strata defined at national level must, in their entirety comprise of all the fishing trips of the metier defined at level 6.
the Baltic Sea (ICES areas III b-d), Mediterranean Sea and the Black Sea, where the resolution shall be level 4;
Regional Fisheries Management Organisations units, providing they are metier-based (in the absence of such definitions, Regional Fisheries Management Organisations shall proceed to appropriate mergers).
The Member State on whose territory the first sale take place, shall be responsible for ensuring that biological sampling occurs according to the standards defined in this Community Programme. If necessary, Member States shall cooperate with the authorities of non EU third countries to set up biological sampling programmes for the landings carried out by vessels flying the third country's flag.
For sampling purpose, only the major metiers need be considered. In order to identify the metiers to be sampled, the following ranking system shall be used at level 6 of the matrix in Appendix IV (1 to 5) on a national basis by Member States using as reference the average values of the two previous years and:
The metier cells shall first be ranked according to their share in the total commercial landings. The shares are then to be cumulated, starting with the largest, until a cut-off level of 90 % is reached. All metiers belonging to the top 90 % shall be selected for sampling,
The exercise shall then be repeated according to the total value of the commercial landings and repeated a third time according to the total effort in days-at-sea. The metiers in the top 90 % not belonging to the previous top 90 % shall be added to the selection,
STECF may add to the selection the metiers not picked up by the ranking system but of special importance in terms of management.
The sampling unit shall be the fishing trip and the number of fishing trips to be sampled shall ensure good coverage of the metier.
Precision values and ranking system are referenced at the same level as the sampling programmes, i.e. at the national metier level for data that are collected through national programmes and at regional metier level for data that are collected through regionally coordinated sampling programmes.
The sampling intensity shall be proportionate to the relative effort and variability in the catches of that metier. The minimum number of fishing trips to be sampled shall never be less than one fishing trip per month during the fishing season for fishing trips of less than two weeks and one fishing trip per quarter otherwise.
When sampling a fishing trip, the species shall be sampled concurrently as follows:
Each species within a region as defined in Appendix II, shall be classified within a group according to the following rules:
:
Species that drive the international management process including species under EU management plans or EU recovery plans or EU long term multiannual plans or EU action plans for conservation and management based on Council Regulation (EC) No 2371/2002 of 20 December 2002 on the conservation and sustainable exploitation of fisheries resources under the common fisheries policy(4),
:
Other internationally regulated species and major non-internationally regulated by-catch species,
:
All other by-catch (fish and shellfish) species. The list of Group 3 species shall be established at the regional level by the relevant regional coordination meeting and agreed by STECF.
Allocation of species to Group 1 and 2 is specified in Appendix VII. The choice of the sampling scheme shall depend on the diversity of species to sample and the operational conditions under which sampling takes place. The sampling design per metier must consider both the periodicity of the sampling events and the sampling scheme to apply. Possible sampling schemes, as described in the following table, comprise:
:
comprehensive sampling of all species,
:
within each time stratum, the sampling events are split in two parts. One part of the sampling events (x %) considers sampling of all species on shore whereas the other part of the sampling events (100-x %) considers only sampling of all Group 1 species,
:
within each time stratum, the sampling events are split in two parts. One part of the sampling events (x %) considers sampling of all Group 1 and Group 2 species on shore, whereas the other part of the sampling events (100-x %) considers only sampling of Group 1 species. In this scheme, Group 3 species have to be sampled at sea.
For any given sample, the sampling scheme shall be recorded (Table 1) along with information on how complete the sampling is:
When sampling a species, the number of individuals measured must ensure quality and accuracy of resultant length frequency. The number of length classes within a sample may be estimated from the approximate length range within it and, from this, the number of fish measured shall lie between 3 × number of length classes and 5 × number of length classes as a first approximation, in the absence of any statistical optimisation of the sampling design.
Other sampling procedures could be used on the condition that there is scientific evidence showing that these procedures will achieve the same objectives as the ones described in point 3(1)(g).
A summary of the sampling protocols carried out by Member States shall be made available to STECF through the national programmes for each metier sampled.
The ranking system referred to in Chapter III section B/B1 3 (1) (b), shall be used to select the metiers in order to estimate discards. In any case, where discards of a given metier are estimated to exceed 10 % of the total volume of catches and this metier is not picked up by the ranking system this metier shall be sampled.
The sampling unit shall be the fishing trip and the number of fishing trips to be sampled shall ensure good coverage of the metier.
Precision values and the ranking system are referenced at the same level as the sampling programmes, i.e. at the national metier level for data that are collected through national programmes and at regional metier level for data that are collected through regionally coordinated sampling programmes.
The sampling intensity shall be proportionate to the relative effort and/or the variability in catches of the metier. The minimum number of fishing trips to be sampled shall not be less than two fishing trips per quarter.
Discards will be monitored for the Group 1, 2 and 3 species, defined in Chapter III section B/B1/3. 1 (f), to estimate the quarterly average weight of discards. Furthermore:
Discards must be the subject of a quarterly estimate of the length distributions when they represent on an annual basis, either more than 10 % of the total catches by weight or more than 15 % of the catches in numbers for the Group 1 and Group 2 species,
When discards take place for species length ranges which are not represented in the landings, age-reading must take place in accordance with the rules set out in Appendix VII.
Where relevant, pilot surveys as referred to in Chapter II B (1) shall be carried out.
A summary of the sampling protocols carried out by Member States shall be made available to STECF through the national programmes for each metier sampled.
For the recreational fisheries targeting the species listed in Appendix IV (1 to 5), Member States shall evaluate the quarterly weight of the catches.
Where relevant, pilot surveys as referred to in Chapter II B (1) shall be carried out to estimate the importance of the recreational fisheries mentioned in point 3(3)(a).
The precision level 2 shall be targeted at the stock level for both Group 1 and Group 2 species. If necessary, specific stock-based samples shall be added if metier-based sampling fails to provide the appropriate precision for length distributions at the stock level.
Data related to quarterly estimates of discards length and age composition for Group 1 and Group 2 species must lead to a precision of level 1.
Weight estimates of Group 1, 2 and 3 species must lead to a precision of level 1.
Data related to annual estimates of the catches in volumes must lead to a precision of level 1.
individual information on age;
individual information on length;
individual information on weight;
individual information on sex;
individual information on maturity;
individual information on fecundity;
using the sampling scheme provided in this Appendix VII.
information on abundance of smolt;
information on abundance of parr;
information on number of ascending individuals.
For maturity and fecundity, calculated as proportion of mature fish, precision of level 3 must be achieved within the age and/or length range, the limits of which correspond to a 20 % and 90 % of mature fish;
For sex ratio, calculated as proportion of females, precision of level 3 must be achieved, up to such an age or length that cumulated landings for the corresponding ages or lengths account for at least 90 % of the national landings for this stock.
The relevant quota must correspond to less than 10 % of the Community share of the TAC or to less than 200 tonnes on average during the previous three years;
The sum of relevant quotas of Member States whose allocation is less than 10 %, must account for less than 25 % of the Community share of the TAC.
number of enterprises;
turnover attributed to fish processing.
Appendix No | Title |
---|---|
I | Geographic stratification by Regional Fisheries Management Organisations |
II | Geographical stratification by region |
III | Fleet segmentation by region |
IV | Fishing activity (metier) by region |
V | Disaggregation levels used for the collection of data |
VI | List of economic variables |
VII | List of biological variables with species sampling specification |
VIII | List of transversal variables with sampling specification |
IX | List of research surveys at sea |
X | List of economic variables for the aquaculture sector |
XI | Sector segmentation to be applied for the collection of aquaculture data |
XII | List of economic variables for the processing industry sector |
XIII | Definition of environmental indicators to measure the effects of fisheries on the marine ecosystem |
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