SPECIFIC CONTRACT No 9 - European Commission · o Mrs Pilar VARA DEL RÍO, Fisheries Adviser. II....
Transcript of SPECIFIC CONTRACT No 9 - European Commission · o Mrs Pilar VARA DEL RÍO, Fisheries Adviser. II....
Jose CERVERA, Pavel SALZ, Ester AZORÍN Report delivery date
7th July 2014
Photographs © Creative commons, courtesy of the authors (Miemo Penttinen,
Jim Champion and Willip Von Ree), who in no way endorse this work or its contents.
COUNTRY REPORT
FIELD WORK MISSION TO SPAIN
JANUARY 2014
This specific contract No 9, SI2.656808 “Field work specific contract for Lithuania, Romania,
Spain and United Kingdom”, has been implemented within the framework contract,
MARE/2009/08 “Assistance for the monitoring of the implementation of national
programmes for the collection, management and use of data in the fisheries sector”,
funded by the DG Mare.
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List of acronyms
AR Annual Report
BDCP Fishing Control Database (Base de datos de control pesquero)
DCF / DCR Data Collection Framework / Regulation
DG MARE Directorate General for Maritime Affaires and Fisheries
EWG Expert Working Group
ICES International Council for the Exploration of the Sea
IEO Spanish Institute of Oceanography (Instituto Español de Oceanografía)
INE National Statistical Institute (Instituto Español de Estadística)
JRC Joint Research Centre
MAGRAMA Ministry of Agriculture, Food and Environment (Ministerio de Agricultura, Alimentación y Medio Ambiente)
NC National Correspondent
NP National Programme
SBS Structural Business Survey
SGP General Secretariat of Fisheries (Secretaría General de Pesca)
ToR Terms of Reference
TR Technical Report
WGHMM Working Group on Hake, Monkfish and Megrim
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Table of Content 1. INTRODUCTION 3 2. GENERAL OVERVIEW, SUMMARY AND CONCLUSIONS 4 3. SUBMISSION OF DATA TO WGHMM IN 2012 6 4. JRC DATA CALLS 10 5. INSTITITUTIONAL ISSUES 13 ANNEX 1. FUEL CONSUMPTION BY SEGMENT 14 ANNEX 2. SCREENSHOT OF DATA UPLOADED BY SPAIN FOR THE 2013 ECONOMIC DATA CALL 15 ANNEX 3. NUMBER OF ENTERPRISES BY SIZE, 2008-2012 16 ANNEX 4. METHODOLOGY FOR THE ESTIMATION OF DISTRIBUTION BY SPECIES. 17 ANNEX 5. SUBMISSION OF TRANSVERSAL DATA UNDER 2014 DATA CALLS FOR EFFORT AND ECONOMICS 18 ANNEX 6. SOURCE OF TRANSVERSAL DATA BY MS 21
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1. INTRODUCTION
Acknowledgements
The team wants to acknowledge the fruitful collaboration and openness of the Ministry of Agriculture,
Food and Environment (MAGRAMA), the Spanish Institute of Oceanography (IEO), National Statistical
Institute (INE) and its staff for their personal contribution to the success of the field work mission. The DCF
team showed in all cases a professional engagement with the objectives of the mission.
Implementation of the mission (counterparts, calendar)
The mission was carried out during 29-30 January 2014. The agenda of the mission, shared with Mr Enrique
de Cárdenas (National Coordinator for the DCF) prior to the mission, was implemented as planned.
Participants from the Spanish Institutions involved in DCF:
1. Ministry of Agriculture, Food and Environment (MAGRAMA)
I. General Secretariat of Fisheries (SGP). Protection of Fisheries Resources Unit
o Mr Enrique DE CÁRDENAS , National Correspondent for the DCF, Deputy Director-General
o Mrs Pilar VARA DEL RÍO, Fisheries Adviser.
II. General Secretariat of Fisheries (SGP). Structural Policies Unit
o Mrs Natalia MORENO LAGUNA, Chief of Marketing Unit
III. General Secretariat of Fisheries (SGP). Control and Inspection Unit
o Mr Héctor VILLA GONZÁLEZ, Deputy Director-General Adjoint
o Mrs Ana LÓPEZ VELASCO, Head of Service Unit
IV. Statistical Unit
o Ms Paloma SEOANE, Deputy Director General, Statistics, MAGRAMA
o Mr Miguel Ángel CORDÓN, Head of Fisheries Statistical Unit
2. Spanish Institute of Oceanography (IEO)
o Mr Pablo ABAUNZA, Head of Fisheries Area
o Mrs Ángeles ARMESTO, Coordination Team for PNDB
Structure of the report
The Country Report is organised according to the requirements of the Terms of Reference (ToR) and
includes the following sections:
Section 2: General overview, summary and conclusions
Section 3: Submission of data to WGHMM in 2012
Section 4: JRC economic data calls
Section 5: Institutional issues
The Country Report is accompanied by 6 annexes.
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2. GENERAL OVERVIEW, SUMMARY AND CONCLUSIONS
The background of this second mission to Spain included a number of questions and concerns of the EC
regarding the Spanish response to several specific data calls. This regards in particular:
- Submission of data on catches to the WGHMM of ICES in May 2012.
- Lack of submission of transversal data to JRC’s call for the Annual Economic Report and the call for
effort regimes in 2012.
In addition the EC wished to be informed about consequences of apparent institutional reorganization
stated in the Annual Report 2012 and budgetary consequences of the austerity measures of the Spanish
government in relation to the national co-financing and implementation of the DCF programme.
The mission draws following conclusions:
1. Until 2011 WGHMM was using landings estimates prepared by IEO and AZTI. As of 2012, Secretaría
General de Pesca (SGP), which is responsible for DCF, has insisted on using only official landings
data, which it provides on the basis of logbooks. WGHMM noted a significant decrease in landings
between 2010 (scientific estimate) and 2011 (official data). In order to avoid break in time series,
WGHMM has made scientific estimates of total EU landings. The difference between the official
total landings (provided by all MS on the basis of logbooks) and the scientific estimate by WGHMM
has been classified as “unallocated catches”. These catches cannot be allocated to any MS or
métier. The method of estimation of the total catches is the responsibility of the WG and it is not
made public.
2. In relation to the landings data produced by the Member States (MS) under DCF it is important to
stress that:
a. DCF does not foresee sampling programmes for estimation of transversal data. DCF calls
for “exhaustive” data collection and therefore it relies on data compiled under the Control
Regulation1, which meets this requirement. Only if exhaustive data collection is not
possible MS may recur to sampling and have to describe their sampling programme. In
practice this occurs very rarely, as the Control Regulation provides exhaustive data, with a
possible exception of the fleet <10m.
b. Almost all MS state in the NPs and ARs that landings (and other transversal) data are
sourced from the data collected under the control regulation, i.e. logbooks usually cross
checked with sales notes.
c. Neither ICES nor IEO could provide references to (refereed) descriptions of methodologies
for scientific estimation of total landings per species, not to speak detailed
disaggregations required by appendix VIII of the DCF regulation. Consequently, it cannot
be determined whether IEO estimates would be “better” than the official SGP data.
1 The Control Regulation may require sampling of the production and effort of the fleet <10m. However, in practice this
fleet is monitored in most MS using sales notes and making assumptions about the relation between sales notes and effort.
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3. As there are various open questions regarding approach to Spanish data in stock assessment, which go
beyond the ToR of the present assignment, it is recommended to analyse the stock assessment
procedure in greater detail.
4. The response to JRC 2012 economic call has been incomplete with respect to fuel use, classification
of fishing enterprises and submission of transversal data, for the reasons explained below:
a. Data on fuel use (in litres) is part of the data collection programme and consequently it is
collected on on-going basis under the economic survey. Data is available in the MAGRAMA
database and presented in annex 1. However, at the time of data submission this variable
was wrongly overlooked as it is classified under transversal variables. Therefore, it was
not submitted due to miscommunication and not due to non-availability.
b. Data on classification of fishing enterprises by size (number of vessels) was submitted for
the country as a whole, but not by segment, because it was not clear how multi-vessel
firms should be allocated to a specific segment if their vessels would belong to different
segments. It is noted that as of 2014 JRC will only call for the national totals and not for the
classification by segment, exactly because of this methodological problem.
c. Submission of transversal data on effort and landings (value and volume) for the
economic data calls was incomplete in 2012 and 2013 because this information could not
be generated from the control data. The mission was informed that Spain has agreed with
the Commission to implement an ‘action plan’, which will make the control data
accessible. It is expected that the problem will be resolved in 2015.
5. Evidence provided by the NC shows that Spain has fully complied with the JRC data calls on fleet
economics and effort in 2014.
6. The institutional changes do not seem to be relevant for the implementation of DCF, as IEO keeps
its scientific status. Cuts in national and EC co-financing are important, but an effort has been made
to maintain the biological sampling at the required level. The size of economic sample (fleet) has
been reduced2.
2 See mission report 2012.
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3. SUBMISSION OF DATA TO WGHMM IN 2012
The EC was informed by the ICES Working Group on Hake, Monkfish and Megrim (WGHMM), about
modifications in the values submitted regarding the relevant species and in particular discrepancies
between “scientific” estimations (from IEO) and “official” (from the SGP) data on catches.
The draft report of WGHMM 2012 states that, in relation to data for the reference year 2011:
The start of the meeting was delayed slightly to allow scientists from IEO to receive an instruction, delivered via
their national institute, regarding the provision of data to the working group. At 09:30 on the first day of the
meeting the working group was advised that the estimates of Spanish landings submitted by IEO for 2011 could
not be used by the working group. Instead, official data for Spanish landings would be provided by the national
administration for fishery statistics (Secretaría General de Pesca - SGP). The instruction was that these official
data should be used in the assessments and that the scientific estimates of landings in 2011 previously provided
by IEO should be disregarded.
Data for Spanish landings were provided to the working group by SGP (via IEO) on Friday 11th May and are
shown in annex T of this report. No information was available on the method by which these data had been
compiled. The data were submitted at very short notice and were not made available following the usual
procedures for the provision of official statistics (i.e. via STATLANT).
The group evaluated these data and quickly concluded that they were unsuitable for use in the models used to
assess the stocks. In many cases the data were not disaggregated to an appropriate level to enable their
inclusion in the assessment models. The level of disaggregation necessary varies between stocks but in some
cases requires data at a quarterly level for the different fleet sectors operating in the fishery. In other instances
the data provided were not disaggregated by species (ie. for monkfish – L. piscatorius and L. budegassa and for
megrim L. whiffiagonis and L. boscii). These species are assessed separately but are managed as a combined
stock. Similarly, for stocks of Nephrops the data were not disaggregated to functional unit level. Some
concerns were raised regarding the validity of the data provided which in some instances indicated a marked
reduction in landings from previous years. It was not possible to attribute these reductions in landings to any
observed changes in the fishery such as a reduction in fishing effort, a marked decline in stock biomass or an
increase in discard levels.
The group concluded that the landings data for 2011 provided by SGP could not be used to update the
assessment models in 2012.
Two issues mentioned in the above excerpt are considered below: the apparent inconsistency between
scientific and official data, and the distribution of a genus by particular species.
Scientific vs “official” data on landings
“Official” data on capacity, effort and landings (transversal data) originate from the monitoring required by
the Control Regulation (logbooks, sales notes, fleet register, landings declarations, VMS). Almost all MS use
the Control Regulation to provide transversal data required under DCF. In Spain the collection and storage
of control data has been facing technical problems, so that the data is not available for the years 2009-2011.
As of 2012 Spain has provided all the requested data. An action plan has been agreed upon between the
Spain and the EC to correct this situation. It is expected that the system will be operational in 2015.
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It seems that IEO (and AZTI) has been producing scientific estimations of landings and their composition.
The estimations of landings are based on sales notes and contacts with the industry3. Contrary to logbooks
data, supplied by SGP, the IEO estimates did not allow determination of the spatial distribution.
In general, the mission notes that:
- IEO could not provide any documentation of methodologies used for the estimation of landings;
- ICES WG reports do not refer to any documents in which such estimations would be described, not
to speak of refereed publications. The only statement in the ICES assessments refers to the sources
of the data, being sales notes and industry organizations;
- The DCF regulation does not require “scientific” collection of data (i.e. surveys) which would allow
estimation of transversal variables, defined in Appendix VIII. In fact, to make reliable estimations of
the listed variables would require a significantly higher sampling intensity.
- During the present project, missions were carried out to 10 MS, of which 8 rely on control data for
the compilation of the transversal variable. This is indicated in the National Plans and Annual
Reports. It was also explicitly confirmed by the National Coordinators from Belgium, Denmark,
Portugal and UK. Census control data is not available only in Italy and Greece. (see annex 6 for
overview of all MS).
- Any scientific estimation of landings, based on sampling, would be by definition stochastic, i.e. it
would provide a confidence interval within which the real value can be expected. Conclusions on
“poor reliability” of official data can be only drawn if the estimate and its standard deviation would
be provided. Such statistical information is not available.
At the Working Group level the official landings data provided by the MS are reviewed and if relevant the
total catch is re-estimated, which may lead to so called ‘unallocated catch’. Formally, unallocated catches
reflect the difference between the total official landings (sum of landings of all MS fishing the stock) and
the scientific estimation of the total catch, prepared by the ICES WG. The scientific “corrections” may
originate from estimations of discards or suspected unreported catch (e.g. based on data on effort, stock
and catch per unit of effort). The catches are unallocated in the sense that they cannot be allocated to any
MS or métier. How these estimations are done is at the discretion of each ICES WG4. The methodologies are
not published.
WGHMM (and WGWIDE) reports relate unallocated catches to the difference between official Spanish data
regarding 2011 and 2012 and the scientific estimation provided to the WGs by IEO and AZTI in previous
years5. However, it is not clear why it should be expected that Spanish catches significantly increased, along
with the increase of the stock, over and above the quota, while there are no statements about the landings
of other MS. In addition, the p.46-47 of the 2013 WGHMM report presents detailed data on catches of
Spanish fleet, while it does not present comparable information for other MS. As there are various open
questions regarding approach to Spanish data in stock assessment, which go beyond the ToR of the
present assignment, it is recommended to analyse the stock assessment procedure in greater detail.
3 WGHMM 2013 report, p. 359. This procedure regards Nephrops. ICES is not informed about the methodology used to estimate the landings volume. 4 Individual MS could make their own estimation of ‘unallocated’ catches and submit them to RDB FishFrame under the heading ‘unallocated catch’. However, ICES has indicated that unallocated catches were never reported to RDB FishFrame by any MS for any stock. 5 E.g. WGHMM report 2013, p.13.
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Estimation of scientific biological indicators
The estimation of the composition (by age, sex and maturity, etc.) is based on the observations by the
“Information and Sampling Network” (Red de Información y Muestreo). IEO has outsourced this activity to
a private company. Every year, the selection of the company is made through a public tender. The tender is
accompanied by a description of the sampling in terms of locations and sample frequencies of catch by
fishery, gear, metier, fishing area and time period. It also includes the number of observations to be carried
out. The sampling is specified as a frequency of measurements by landing location per region
(Mediterranean, CECAF/Cádiz, CECAF/Tenerife, Mediterranean/Tuna, Bay of Biscay/Coruña, Canary
Islands/Tuna) as well as per programme (ICES). The results of the sampling (i.e. number of specimen
measured6, either at sea or on shore) in relation to the national plan are presented in the technical reports.
The experts at IEO and AZTI compile the data (age, sex, maturity, length and weight) from the Information
and Sampling Network by aggregation of results at port level. There is no statistical estimation model used
to produce data. This means that relative distribution by each characteristic is directly taken from the
sampling results.
The consultants have checked that the WGHMM Report 2013 includes Spanish measurements of:
- Lengths for monkfish by species (L.pisc., L.bude.);
- Lengths and ages for megrim by species (L.whiff, L.boscii);
- Lengths for hake;
- Lengths for nephrops except for functional area FU 23 – 24.
During the WGHMM meeting of 2012 the Spanish experts were not able to make estimates of the specific
species of monkfish and megrim. The catches of individual species of monkfish and megrim are estimated
by IEO in 2012 on the basis of the results of port and at sea surveys as described below. The distribution of
monkfish and megrim catches by species is based on the sample distribution found in market (carried out
by an external company IPD) and sea surveys taking into account métiers and seasons.
The methodology to estimate the distribution by species was provided in the form of bibliographical
references. In particular, Working Document to the ICES Working Group on the Assessment of Southern
Self Stocks of Hake, Monk and Megrim (WGHMM), Copenhagen, 5-11 May 2011. Annex B, WD27 and more
specifically: Annex B: Working Documents presented to WGHMM 2011. WD2: Sampling procedures for the
proportion estimates of Lophius piscatorius and Lophius budegassa in the Spanish landings. B y R. Gancedo,
R. Morlán, B. Patiño and A.C. Fariña (in Annex).
The methodology described in this paper about monkfish is applicable to the estimation of landings by
species of all species of ICES in which there is confusion between species of the same genus (as also
happens in the case of megrims). It consists in the following steps:
- Data collection: at this stage, commercial categories are not regularly separated in the Spanish
landings, or at least discrimination by species is variable from port to port, and are recorded
together as Lophius spp. The separation is mainly made during the final market stage due to
different appreciation and economic value in the fish market.
- The proportion per species is calculated for each trip/vessel in the sample.
6 Target number of measurements is specified in the National Plans. 7 http://www.ices.dk/community/groups/Pages/WGHMM.aspx.
9
- Individual data are classified by length classes. Weight is estimated by applying model of the
length-weight relationship of the form W = a·Lb
- Sample estimates are extrapolated to population proportions by considering length distributions,
provided by AZTI for the ports in the Basque Country. To gross-up sample estimates, the
distributions are successively raised to monthly landings at the port and metier level and then to
monthly landings at the region level (i.e. extrapolating to the ports where samples were not taken
– this information is available from Control Data).
This general procedure has some specificities mentioned in the ICES paper (see annex 4), but the procedure
is quite standard in any stratified random sampling. The coverage of ports is very large in the North-West
regions.
Two caveats that could be mentioned regarding the estimation procedure: first, the procedure for
randomly selecting trips/vessels is not described; second, except for La Coruña and Ribeira, only one métier
was selected in each port (information from the 2010 sampling plan).
Data problems in 2013 WGHMM report
Although this report refers again to the official data submitted by SGP and estimation of “unallocated
catches”, the report does not mention any data problems related to Spain in the annex V “Stock Data
Problems Relevant to Data Collection”.
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4. JRC DATA CALLS
Coverage reports of JRC of 2012 regarding the economic data call indicate that Spain has not submitted
several indicators:
a. Energy consumption (litres).
b. Composition of enterprises by number of vessels.
c. Fishing effort (except kW-days for 2012)
Economic data call - Energy consumption
The NP 2011-2013 (Revision 2013) states that energy consumption is compiled within the economic survey to
the fishing fleet8. Fuel use is indeed one of the variables included in the economic survey to the fishing fleet
carried out by the MAGRAMA’s Directorate of Statistics.
This information was provided by the Statistics Directorate to the SGP. The data on 2008-2011 was provided
to the mission (see Annex 1).
However, SGP apparently did not submit the data to JRC, as it is included under transversal variables (effort
template) and SGP wrongly assumed that all those variables would be forthcoming from the control data,
which could not be submitted. The Spanish NC was informed about the overall quality of the Spanish
submission by JRC in an email of 13.3.2013. The file which was sent to him specified all missing data9.
However, it was noted that the variable ‘Energy consumption’ is not mentioned in the TR 201210 neither
under transversal variables (table III-F-1) nor under economic variables (III-B-3). The text of TR 201211
mentions use of energy only under the environmental indicator nr.9, but not in the relation to economic
indicators, as required in appendix VI of Com. Decision 93/2010. This also shows the misinterpretation which
existed regarding this indicator. There is no other technical reason for the lack of this information.
Economic call - Composition of enterprises by number of vessels
Data on classification of fishing enterprises by size (number of vessels) was submitted for the country as a
whole (variable Fishent-tot), but not by segment, because it was not clear how multi-vessel firms should be
allocated to segments. It is noted that as of 2014 JRC will only call for the national totals and not for the
classification by segment, exactly because of this methodological problem. This information was also
provided to the mission for the year 2012 and was sent to JRC in data call time and correct format. (Annex
3).
Transversal variables – effort and economic data call
The following table shows that all data were submitted as requested by the JRC calls for fleet economic and
effort data in 2014. The problems which occurred in the preceding years have been resolved. JRC also
confirmed that errors shown in the screen shots in Annex 5 have been of technical nature and all have been
resolved. As of June 2014 the data quality of Spanish submission has not yet been evaluated by STECF.
8 PROGRAMA DE RECOPILACION Y GESTION DE DATOS DE ESPAÑA PERIODO 2011-2013 (Revisión Año 2013), 30.10.2012, p.20-21. 9 Information provided by JRC. 10 España, Informe Técnico 2012, Tablas 30 mayo 2013 11 Informe técnico del programa de recopilación, gestión y uso de datos del sector pesquero de España año 2012
11
Table 1. Overview of data gaps in submissions in 2013 and 2014
Missing data - call 2013
Submitted data -call 2013
Missing data - call 2014
Submitted data -call 2014
Effort regime data call
Landings 2010-2011 2003-2008 All data submitted on 4-6-2014
Discards 2003, 2010-2011 2004-2009
Age of vessel 2009-2011 2003-2008
Landings by rectangle 2003-2011
Nominal effort 2000-2001 and 2010-2011
2002-2009
Effective effort by rectangle
2010-2011 2003-2009
Economic data call
Effort by segment No data kW-days 2012 – FAO Level3_4
All data submitted on 4-6-2014 Value of landings /
species
No data
Volume of landings / species
2008-2011 2012
Sources:
- Effort data call – JRC, DCF Fishing Effort Regimes Data Call 2012 Coverage report, 2012, p.69-70
- Economic call - 2013 DCF Call for Economic Data on the EU Fishing Fleet, coverage report, p.86
- Effort and Economic call – 2014 – Information from NC, see annex 5
The NC and the representative of the Control Unit explained that the Spanish database on control data is
undergoing a major overhaul (‘action plan’), which was developed and agreed upon in cooperation with the
DG Mare. If the deadlines are met, it will be operational in 2015. This will further facilitate the delivery of
transversal data. As indicated in the above table, Spain delivered all data requested by JRC data calls in
2014. The consultant requested a copy of the ‘action plan’, but did not receive it, apparently because this is
a bilateral agreement between EC and Spain. While the ‘action plan’ will assure smooth provision of data in
the future, it is uncertain that it will be possible to reproduce historical data on effort (by métier, segment
and area) and landings (by segment, species and area), which is presently missing. It remains to be seen
whether it will be possible to incorporate logbooks, sale notes and other Control Regulation documents
from previous years in the new system. It is not clear to which extent all historical documents are digitalized
and if so compatible with the new system. The consultant wishes to stress that this is primarily an issue
concerning the implementation of the Control Regulation and not DCF.
It is recommended to closely monitor the implementation of the action plan until 2015. Setting concrete
milestones (if not already done) based on the submission of the missing data mentioned above would be
useful in ensuring that the information targets are met.
12
Other calls
Fish processing industry
The JRC Coverage Report on the Fish Processing Industry for 201312 mentions the lack of submission of
certain variables: male/female employees, imputed value of unpaid labour, depreciation of capital, debt and
total value of assets. It was already mentioned in the consultant’s report of April 201213 that data on the
processing industry are collected by the National Statistical Institute in the context of the SBS Regulation
(Com. Reg. 251/2009) which does not foresee collection of these indicators. Considering that fish processing
is just a small part of the SBS and SBS requirements have been defined under the Eurostat and related
statistics legislation, it does not seem possible for the NSI to include additional indicators in the survey. A
complementary survey to collect the specific DCF indicators has not been considered in order not increase
further the administrative burden to the industry. The methodology is adequately described by the National
Statistical Institute14.
It has been mentioned by the Spanish authorities that there is work in progress to try to solve this issue.
Various meetings have been held between NSI and the Statistical unit of MAGRAMA. The NC has indicated
that the Statistical unit is now estimating the employment by gender and the imputed value of unpaid
labour till 2012 and these indicators will be submitted with the 2014 data call on fish processing (data till
2012). As for the other variables, it is being studied if they can be collected under SBS or else from other
sources like commercial registers.
12 http://datacollection.jrc.ec.europa.eu/c/document_library/get_file?uuid=db6db11b-6115-4c6f-abdb-
86dfb6caf908&groupId=10213, page 63 13 Specific contract SI2.611388. 14 http://www.ine.es/daco/daco42/encindem/metoeiae.pdf
13
5. INSTITITUTIONAL ISSUES
Position of IEO under the new administration
According to the TR 2012, IEO falls under the Ministerio de Economía y Competitividad, while previously it
was part of Ministerio de Ciencia e Innovación. This is a consequence of the transfer of Secretaría de Estado
de Investigación, under which IEO resides. However, IEO maintains its formal status of ‘organismo público
de investigación (OPI)’. Consequently the apparent transfer from one ministry to another does not have
any consequences.
Data confidentiality
In various RCMs Spain has repeatedly expressed its concern regarding the confidentiality of data provided
inter alia to the RDB-FishFrame databases of RCGs (ex-RCMs)15: “Spain is clarifying its concerns related to
confidentiality, access, security and use of the data.” (p.52)
This is a consequence of the fact that submission of data on vessel power and tonnage is mandatory for the
RDBs, while it was optional for earlier submission to ICES. Spain considers the confidentiality guaranties
currently in force at RCMs and ICES WGs inadequate, as they do not go beyond the signed confidentiality
declaration by participating scientists.
The NC mentioned that in some cases it has been demonstrated that giving data on vessels size, it is
possible to identify individual vessels.
For biological data, Spain has no problems in transmitting biological parameters; however the SGP as well
as IEO recommended to keep an embargo of the public dissemination of data so the scientist can publish
their research results.
For economic and transversal data, the Spanish Institutions would agree to release individual data for
specific research projects with the condition that data are not stored in data bases and deleted at the end
of the study.
It seems necessary to review in detail the confidentiality practices of Eurostat (or other statistical
institutions holding personal data) and translate them properly to data handling practices under DCF, in
particular to RCMs.
Budget Issues
IEO has been seriously affected by budget cuts, both at the National and EC level. In particular there was a
decrease of 8.5% of the financing provided by DCF due to the underspending of the budget for the previous
year (2012). This underspending was principally due to the decrease in the national budget for personnel
costs and subsequent salary cuts. Despite these budget cuts and considering the importance of maintaining
the sampling size, the IEO has kept similar sample sizes for operations by using its internal budget. Only a
reorganization and a slight decrease in the number of on shore samplings has been observed.
The sample size of the economic survey to the fishing fleet has been reduced from 920 vessels in 2008-9 to
422 vessels in 2011, as stated in the subsequent TRs.
15 E.g. Report of the Regional Co-ordination Meeting for the North Atlantic (RCM NA) 2012, p.52
14
ANNEX 1. FUEL CONSUMPTION BY SEGMENT
Total litres YEAR
FISHING_TECH VESSEL_LENGTH 2008 2009 2010 2011
DFN VL0010 232,846 125,632 67,850
VL1012 1,050,452 146,797 82,427
VL1218 2,317,540 4,021,917 634,500 1,877,700
VL1824 25,274,644 2,099,440 2,018,333 2,502,000
VL2440 37,061 2,122,023 1,100,105
DFN Total 28,912,543 8,515,809 3,752,938 4,529,977
DTS VL0010 8,258,982
VL0612 832,000 862,650 489,667 516,946
VL1012 26,714,913
VL1218 131,555,461 18,803,681 24,465,525 18,216,687
VL1824 86,860,479 65,710,471 62,836,500 58,101,036
VL2440 92,411,029 270,048,593 196,817,932 297,747,118
VL40XX 30,509,138 80,096,058 91,912,366 105,915,103
DTS Total 377,142,003 435,521,454 376,521,990 480,496,890
HOK VL0010 19,815,607 676,542 597,167 160,105
VL0612 4,248,889 2,849,610 2,840,867 1,763,538
VL1012 3,360,686 1,299,006 766,001 914,650
VL1218 20,865,909 6,768,257 4,569,575 6,474,990
VL1824 12,907,333 11,037,980 6,540,710 9,751,299
VL2440 2,801,750 60,204,827 63,248,530 66,256,405
VL40XX 29,904,590 21,682,319 29,189,000 32,910,449
HOK Total 93,904,764 104,518,540 107,751,849 118,231,436
MGP VL1824 2,711,925
MGP Total 2,711,925
PGP VL0612 73,775
VL1218 534,638
VL2440 19,835,860 23,753,310
PGP Total 19,835,860 24,361,723
PMP VL0006 6,556,505 0 62,225
VL0010 13,859,011 18,915,523 15,958,803
VL0612 6,234,494 6,116,309 7,597,082
VL1012 14,383,395 2,190,808 5,499,055 3,060,035
VL1218 4,455,012 14,481,564 7,885,050 17,790,820
VL1824 16,445,259
VL2440 6,627,755 16,849,956 1,521,500 2,460,716
VL40XX 1,037,156
PMP Total 42,948,577 60,172,338 39,937,437 46,929,681
PS VL0006 3,133,333
VL0010 249,023 183,883 39,787
VL0612 648,200 463,260 87,150 219,267
VL1012 384,480 509,425 447,539
VL1218 7,149,155 10,454,591 5,823,806 10,010,481
VL1824 93,945,683 10,396,841 8,231,414 16,954,150
VL2440 27,153,701 28,299,126 46,821,680 15,480,026
VL40XX 86,953,192 109,745,847 120,059,465
PS Total 132,030,073 137,200,514 171,403,205 163,210,714
Grand Total 674,937,960 745,928,654 719,203,280 840,472,345
Source: Statistics Directorate, MAGRAMA
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ANNEX 3. NUMBER OF ENTERPRISES BY SIZE, 2008-2012
Number of enterprises
Number of vessels - total
Of which inactive vessels
2008
1 vessel 11.248 11.248 2.995
2-5 vessels 841 1.828 317
6+ vessels 4 39
2009
1 vessel 9.902 9.902 1.633
2-5 vessels 710 1.561 18
6+ vessels 4 38
2010
1 vessel 9.659 9.659 761
2-5 vessels 686 1.498 93
6+ vessels 6 52
2011
1 vessel 9.438 9.438 900
2-5 vessels 652 1.403 107
6+ vessels 5 51
2012
1 vessel 9.146 9.146 1.349
2-5 vessels 625 1.350 247
6+ vessels 5 48 21
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ANNEX 4. METHODOLOGY FOR THE ESTIMATION OF DISTRIBUTION BY
SPECIES.
Working Document to the ICES Working Group on the Assessment of Southern Shelf Stocks of Hake, Monk
and Megrim (WGHMM), Copenhagen, 5-11 May 2011
Sampling procedures for the proportion estimates of Lophius piscatorius and Lophius budegassa
in the Spanish landings
R. Gancedo1, R. Morlán2, B. Patiño3, A.C. Fariña2
1IEO, Centro Oceanográfico de Santander, Promontorio de San Martín s/n, 39004 Santander, Spain
2IEO, Centro Oceanográfico de A Coruña, Pº Mº Alcalde Francisco Vázquez Nº 10, 15001 A Coruña, Spain
3IEO, Centro Oceanográfico de Vigo, Avda. de Beiramar 37, 36202 Vigo, Spain
18
ANNEX 5. SUBMISSION OF TRANSVERSAL DATA UNDER 2014 DATA CALLS
FOR EFFORT AND ECONOMICS
Economic data call
19
Effort data call
The screen shots below indicate that data was uploaded with errors. However, the NC stated in his
comments that all causes of these ‘error’ were explained to the chair of the WG, who recognised that the
provided data was correct.
21
ANNEX 6. SOURCE OF TRANSVERSAL DATA BY MS
As shown in table 1, transversal data submitted by MS under the various DCF data calls, is mostly based on
census, sourced from information compiled for the purposes of the Control Regulation (logbooks, fleet
register, etc.). This implies that the submitted DCF data is fully consistent with the ‘official data’.
In addition it should be noted that many (if not most) MS, the national correspondent is a staff member of
the ministry which is responsible for fisheries management, including DCF and control. The ministry ensures
that no major discrepancies between DCF and control data exist (e.g. France).
Table 1. Approach to collection of transversal data
MS Approach to data collection
BE A (2011)
BG A (2011)
CY A (2011)
DE A, B for vessels <=8m
DK A (2011)
ES A (2011)
EE A
FI A
FR A >10m. C<10m, value and prices C >=10m (2011)
GBR A
GR A (capacity), B all other variables
IE A
IT B
LV A (2011)
LT A
MT A, B for vessels <= 10m
ND A
PL A
PT A (2011), B = energy consumption
RO A
SI A
SE A Source: DCF Annual reports 2012 (or 2011 if stated) A - Census; B - Probability Sample Survey; C - Non-Probability Sample Survey Census implies using the full set of logbooks, sales notes, landings declarations, VMS and Fleet register.
22
Distinction between scientific and official data
As stated above data on capacity, effort and landings (by species and areas, i.e. stocks) originates from
‘official sources’ (logbooks, etc.).
Scientific component of the DCF data are stock and métier related parameters regarding: age, weight, sex,
length, fecundity and discards. These measurements allow estimations of indicators length@age,
maturity@age, maturity@length, sex-ratio@age, sex-ratio@lenght and weight@age. This data are input
for the age-class (or length-class) structured biological models (VPA, virtual population analysis).
ICES guidelines for data submission to RDB FishFrame confirm that landings and effort data are based on
official (logbook) sources, while separate information can be added for misreporting (see box below).
Information on misreporting has never been provided by any MS.
Source: Jansen, T. (Ed). 2009. Definition of Standard Data-Exchange Format for Sampling, Landings, and Effort Data from Commercial Fisheries. ICES Cooperative Research Report No. 296. 43 pp.