Member State report / Art11 / 2014-2020 / D3 / Belgium / NE Atlantic: Greater North Sea

Report type Member State report to Commission
MSFD Article Art. 11 Monitoring programmes (and Art. 17 updates)
Report due 2014-10-15; 2020-10-15
GES Descriptor D3 Commercial fish and shellfish
Member State Belgium
Region/subregion NE Atlantic: Greater North Sea
Reported by Reporter not found
Report date Date not found; 2020-10-29
Report access
2014 data
2020 data
Monitoring programme Monitoring programme name
MP_D3
Monitoring programme Reference existing programme
Monitoring programme Marine Unit ID
Q4e - Programme ID
ANSBE-D3 Commercial fish/and shellfish
Q4f - Programme description
The Belgian MSFD monitoring programme ‘Commercial fish and shellfish’ aims at assessing the following ETs: • ET19 – All commercial fish stocks managed through the CFP are being managed in a way that minimally meets the maximum sustainable yield. This assessment should be performed on the basis of regional fish stocks, and not on a national level • ET20 – All commercial fish and shellfish stocks are within safe biological limits, with an age (when available) or size (if ages not available) distribution indicative for a healthy stock, and the stocks should be exploited on a stable, long term, with full reproductive capacity • ET21 – Shellfish stocks are being managed sustainably • ET22 – All commercial fish and shellfish stocks have complete reproductive capacity • ET23 – Fishing mortality values and spawning stock biomasses are within safe biological limits (F below or egual to reference points for fishery mortality; SSB above or equal to reference points for spawning stock biomass) or show positive of stable trends in survey abundance and negative or stable trends in survey CPU • ET24 – Stocks that are not within safe biological limits yet should at least show trends of movement in the direction of the reference points • ET25 – When data on a stock are even insufficient to evaluate trends in survey CPUE and abundance, these stocks will be placed in the category of data deficient stocks and discussions will be initiated regarding alternative evaluation methods. This category will be revised after each 6 years One sub-programme can be discerned: • ANSBE-D3 Commercial fish-SP13 (delivering data to assess ET19 to 25), targeting the fish stock assessment through the BTS and the DYFS surveys
Q5e - Natural variability
  • Quantiative
Q5d - Adequacy for assessment of GES Q5d - Adequate data
Y
Q5d - Adequacy for assessment of GES Q5d - Established methods
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate understanding of GES
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate capacity
Y
Q5f - Description of programme for GES assessment
Q5g - Gap-filling date for GES assessment
By2014
Q5h - Plans to implement monitoring for GES assessment
N.A.
Q6a -Relevant targets Q6a - Environmental target
Target 19 Target 20 Target 21 Target 22 Target 23 Target 24 Target 25
Q6a -Relevant targets Q6a - Associated indicator
Target 19 Target 20 Target 21 Target 22 Target 23 Target 24
Q6b - Adequacy for assessment of targets Q6b_SuitableData
Y
Q6b - Adequacy for assessment of targets Q6b_EstablishedMethods
Y
Q6b - Adequacy for assessment of targets Q6d_AdequateCapacity
Y
Q6c - Target updating
N
Q6d - Description of programme for targets assessment
N.A.
Q6e - Gap-filling date for targets assessment
By2014
Q6f - Plans to implement monitoring for targets assessment
N.A.
Q7a - Relevant activities
Q7b - Description of monitoring of activities
Q7c - Relevant measures
Q7e - Adequacy for assessment of measures Q7d - Adequate data
Q7e - Adequacy for assessment of measures Q7d - Established methods
Q7e - Adequacy for assessment of measures Q7d - Adequate understanding of GES
Q7e - Adequacy for assessment of measures Q7d - Adequate capacity
Q7e - Adequacy for assessment of measures Q7d - Addresses activities and pressures
Q7e - Adequacy for assessment of measures Q7d - Addresses effectiveness of measures
Q7d - Description of monitoring for measures
Q7f - Gap-filling date for activities and measures
By2014
Q8a - Links to existing Monitoring Programmes
  • CFP-DC-MAP
Reference sub-programme Sub-programme ID
Reference sub-programme Sub-programme name
Mobile species - population characteristics
Q4g - Sub-programmes Sub-programme ID
Q4g - Sub-programmes Sub-programme name
Mobile species - population characteristics
Q4k - Monitoring purpose
Q4l - Links of monitoring programmes of other Directives and Conventions
Q5c - Features Q5c - Habitats
Q5c - Features Q5c - Species list
  • FishAll
Q5c - Features Q5c - Physical/Chemical features
Q5c - Features Q5c - Pressures
  • ExtractSpeciesFishShellfish
Q9a - Elements
Q5a - GES criteria Relevant GES criteria
  • 3.1
  • 3.2
  • 3.3
Q5b - GES indicators Relevant GES indicators
Q9b - Parameters monitored (state/impact) Species distribution
Q9b - Parameters monitored (state/impact) Species population size
Q9b - Parameters monitored (state/impact) Species population characteristics
Q9b - Parameters monitored (state/impact) Species impacts
Q9b - Parameters monitored (state/impact) Habitat distribution
Q9b - Parameters monitored (state/impact) Habitat extent
Q9b - Parameters monitored (state/impact) Habitat condition (physical-chemical)
Q9b - Parameters monitored (state/impact) Habitat condition (biological)
Q9b - Parameters monitored (state/impact) Habitat impacts
Q9b - Parameters monitored (pressures) Pressure input
Q9b - Parameters monitored (pressures) Pressure output
Q9b - Parameters monitored (activity) Activity
Q9b Parameters monitored (other) Other
Q41 Spatial scope
Q4j - Description of spatial scope
Marine Unit IDs
  • ANS-BE-MS-1
Q4h - Temporal scope Start date- End date
-
Q9h - Temporal resolution of sampling
Q9c - Monitoring method
Q9d - Description of alteration to method
Q9e - Quality assurance
Q9f - Quality control
Q9g - Spatial resolution of sampling Q9g - Proportion of area covered %
Q9g - Spatial resolution of sampling Q9g - No. of samples
Q9i - Description of sample representivity
Q10a - Scale for aggregation of data
Q10b - Other scale for aggregation of data
Q10c - Access to monitoring data Q10c - Data type
Q10c - Access to monitoring data Q10c - Data access mechanism
Q10c - Access to monitoring data Q10c - Data access rights
Q10c - Access to monitoring data Q10c - INSPIRE standard
Q10c - Access to monitoring data Q10c Date data are available
Q10c - Access to monitoring data Q10c - Data update frequency
Q10d - Description of data access
Descriptor
D3
D3
D3
D3
D3
D3
D3
D3
D3
D3
D3
Monitoring strategy description
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
The monitoring focuses on in situ data collection of biological data of species and habitats typical for demersal fisheries (mainly beam trawl) and has been approved by the EU under the Data Collection Framework. The methodology to collect the data and to assess the quality are coordinated on EU level under the regional approach of the European Collection Framework (Regional Coordination Groups).
Coverage of GES criteria
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Gaps and plans
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Focus is put on demersal species and beam trawl fisheries, the other fleet segments are not selected for monitoring. The selection of the segments and species is according to rules & procedures established and agreed by the EU (and regionally coordinated).
Related targets
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
  • D3.T1
  • D3.T2
  • D3.T3
  • D3.T4
Coverage of targets
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Related measures
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 23A - 'Better coordination mechanism between the Flemish and Federal authority on fisheries'
  • 27A - 'Increased control of recreational fisheries'
  • 27B - 'Monitoring of the size of recreational fishing'
  • 27C - 'Supporting the discussion about simplification of the conversion of recreational fishermen into commercial fishermen'
  • 32 - 'Species-specific approach for sharks and rays'
  • 8A - 'National ban on fishery ships > 70 GT within a 3 nautical miles area'
  • 8B - 'TAC and quota'
  • 8D - 'Multiannual restoration and management plans for some stocks'
  • 8E - 'Inspection/follow-up/ monitoring of fisheries'
  • 8F - 'ICES supervises the quotas and the stock analysis'
  • 8G - 'Disappearance of discards (in the revised CFP)'
  • 8H - 'Verplicht streven naar MSY (in hernieuwd GVB)'
  • 8I - 'Multispecies-quota en -beheer (in hernieuwd GVB)'
  • 8J - 'Data collection framework + multiannual programmes for data collection'
Coverage of measures
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Related monitoring programmes
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
  • ANSBE-P11-Fish-2-commercial
  • ANSBE-P3-Fish-1-population
Programme code
ANSBE-P11-Fish-2-commercial
ANSBE-P11-Fish-2-commercial
ANSBE-P11-Fish-2-commercial
ANSBE-P11-Fish-2-commercial
ANSBE-P11-Fish-2-commercial
ANSBE-P11-Fish-2-commercial
ANSBE-P11-Fish-2-commercial
ANSBE-P3-Fish-1-population
ANSBE-P3-Fish-1-population
ANSBE-P3-Fish-1-population
ANSBE-P3-Fish-1-population
Programme name
Fisheries-dependent observer-at-sea programme - Common Fisheries Policy
Fisheries-dependent observer-at-sea programme - Common Fisheries Policy
Fisheries-dependent observer-at-sea programme - Common Fisheries Policy
Fisheries-dependent observer-at-sea programme - Common Fisheries Policy
Fisheries-dependent observer-at-sea programme - Common Fisheries Policy
Fisheries-dependent observer-at-sea programme - Common Fisheries Policy
Fisheries-dependent observer-at-sea programme - Common Fisheries Policy
Fish - scientific surveys - Common Fisheries Policy
Fish - scientific surveys - Common Fisheries Policy
Fish - scientific surveys - Common Fisheries Policy
Fish - scientific surveys - Common Fisheries Policy
Update type
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Old programme codes
  • ANSBE-D3-Commercial-fish-SP13
  • ANSBE-D3-Commercial-fish-SP13
  • ANSBE-D3-Commercial-fish-SP13
  • ANSBE-D3-Commercial-fish-SP13
  • ANSBE-D3-Commercial-fish-SP13
  • ANSBE-D3-Commercial-fish-SP13
  • ANSBE-D3-Commercial-fish-SP13
  • ANSBE-D1-4-Fish-SP3
  • ANSBE-D1-4-Fish-SP3
  • ANSBE-D1-4-Fish-SP3
  • ANSBE-D1-4-Fish-SP3
Programme description
Fisheries Observer Programme: On commercial vessels, a sea-going observer collects data on species, numbers, length and weight of the caught fish. Samples are brought to the lab for individual analysis of length, weight, sex, maturity and age. The observer also documents recordings of certain bycatch species (protected fish, birds, turtles or mammals). Based on the selection criteria described by the Data Collection Framework (DCF), and considering the importance of the Belgian beam trawl fleet targeting demersal species (TBB_DEF), Belgium focusses on the collection of fishery-dependent data for this fleet (both fleet segments TBB_DEF_>221 kW and TBB_DEF_<=221 kW coastal vessels and euro cutters). For the beam trawl targeting crustaceans (TBB_CRU), representing 5% of the landings, Belgium has obtained a derogation in area IV (North Sea) and VIId (Eastern English Channel). For the bottom otter trawls (OTB) in VIIfg (Celtic Sea and Bristol Channel), Belgium also obtained a derogation. Thus, both are not included in the monitoring programme. Setting up discard sampling programmes for this fishery is disproportionate compared to the added value to the international data collection. Moreover, it is of limited importance to the Belgian fisheries (8% of landings). The remaining fisheries such as Scottish seine (SSC), Boat dredge (DRB), trammel nets (GTR) and gill nets (GNS) were also not included because 1) they comprise less than 10% of the landings; 2) the number of vessels within these fleets is often too small to guarantee privacy of the collected data and/or 3) there is no space for taking observers on board. The two fleet segments (TBB_DEF_>221 kW and TBB_DEF_<=221 kW) are treated as two separate strata in the Belgian at sea sampling programme. Catch information (landings and discards are covered) is obtained through on-board observation. Four ILVO observers assure a sampling coverage of on average 1% of all fishing hours (approximately 40 trips on an annual basis). The sampling effort targets for one year are set at 8 trips for the TBB_DEF_<=221 kW fleet segment and 34 trips for the TBB_DEF_>221 kW fleet segment. This programme contributes to environmental targets D3.1, D3.2, D3.3, D3.4 and D1.4. (former programme ANSBE-D3-Commercial-fish-SP13 )
Fisheries Observer Programme: On commercial vessels, a sea-going observer collects data on species, numbers, length and weight of the caught fish. Samples are brought to the lab for individual analysis of length, weight, sex, maturity and age. The observer also documents recordings of certain bycatch species (protected fish, birds, turtles or mammals). Based on the selection criteria described by the Data Collection Framework (DCF), and considering the importance of the Belgian beam trawl fleet targeting demersal species (TBB_DEF), Belgium focusses on the collection of fishery-dependent data for this fleet (both fleet segments TBB_DEF_>221 kW and TBB_DEF_<=221 kW coastal vessels and euro cutters). For the beam trawl targeting crustaceans (TBB_CRU), representing 5% of the landings, Belgium has obtained a derogation in area IV (North Sea) and VIId (Eastern English Channel). For the bottom otter trawls (OTB) in VIIfg (Celtic Sea and Bristol Channel), Belgium also obtained a derogation. Thus, both are not included in the monitoring programme. Setting up discard sampling programmes for this fishery is disproportionate compared to the added value to the international data collection. Moreover, it is of limited importance to the Belgian fisheries (8% of landings). The remaining fisheries such as Scottish seine (SSC), Boat dredge (DRB), trammel nets (GTR) and gill nets (GNS) were also not included because 1) they comprise less than 10% of the landings; 2) the number of vessels within these fleets is often too small to guarantee privacy of the collected data and/or 3) there is no space for taking observers on board. The two fleet segments (TBB_DEF_>221 kW and TBB_DEF_<=221 kW) are treated as two separate strata in the Belgian at sea sampling programme. Catch information (landings and discards are covered) is obtained through on-board observation. Four ILVO observers assure a sampling coverage of on average 1% of all fishing hours (approximately 40 trips on an annual basis). The sampling effort targets for one year are set at 8 trips for the TBB_DEF_<=221 kW fleet segment and 34 trips for the TBB_DEF_>221 kW fleet segment. This programme contributes to environmental targets D3.1, D3.2, D3.3, D3.4 and D1.4. (former programme ANSBE-D3-Commercial-fish-SP13 )
Fisheries Observer Programme: On commercial vessels, a sea-going observer collects data on species, numbers, length and weight of the caught fish. Samples are brought to the lab for individual analysis of length, weight, sex, maturity and age. The observer also documents recordings of certain bycatch species (protected fish, birds, turtles or mammals). Based on the selection criteria described by the Data Collection Framework (DCF), and considering the importance of the Belgian beam trawl fleet targeting demersal species (TBB_DEF), Belgium focusses on the collection of fishery-dependent data for this fleet (both fleet segments TBB_DEF_>221 kW and TBB_DEF_<=221 kW coastal vessels and euro cutters). For the beam trawl targeting crustaceans (TBB_CRU), representing 5% of the landings, Belgium has obtained a derogation in area IV (North Sea) and VIId (Eastern English Channel). For the bottom otter trawls (OTB) in VIIfg (Celtic Sea and Bristol Channel), Belgium also obtained a derogation. Thus, both are not included in the monitoring programme. Setting up discard sampling programmes for this fishery is disproportionate compared to the added value to the international data collection. Moreover, it is of limited importance to the Belgian fisheries (8% of landings). The remaining fisheries such as Scottish seine (SSC), Boat dredge (DRB), trammel nets (GTR) and gill nets (GNS) were also not included because 1) they comprise less than 10% of the landings; 2) the number of vessels within these fleets is often too small to guarantee privacy of the collected data and/or 3) there is no space for taking observers on board. The two fleet segments (TBB_DEF_>221 kW and TBB_DEF_<=221 kW) are treated as two separate strata in the Belgian at sea sampling programme. Catch information (landings and discards are covered) is obtained through on-board observation. Four ILVO observers assure a sampling coverage of on average 1% of all fishing hours (approximately 40 trips on an annual basis). The sampling effort targets for one year are set at 8 trips for the TBB_DEF_<=221 kW fleet segment and 34 trips for the TBB_DEF_>221 kW fleet segment. This programme contributes to environmental targets D3.1, D3.2, D3.3, D3.4 and D1.4. (former programme ANSBE-D3-Commercial-fish-SP13 )
Fisheries Observer Programme: On commercial vessels, a sea-going observer collects data on species, numbers, length and weight of the caught fish. Samples are brought to the lab for individual analysis of length, weight, sex, maturity and age. The observer also documents recordings of certain bycatch species (protected fish, birds, turtles or mammals). Based on the selection criteria described by the Data Collection Framework (DCF), and considering the importance of the Belgian beam trawl fleet targeting demersal species (TBB_DEF), Belgium focusses on the collection of fishery-dependent data for this fleet (both fleet segments TBB_DEF_>221 kW and TBB_DEF_<=221 kW coastal vessels and euro cutters). For the beam trawl targeting crustaceans (TBB_CRU), representing 5% of the landings, Belgium has obtained a derogation in area IV (North Sea) and VIId (Eastern English Channel). For the bottom otter trawls (OTB) in VIIfg (Celtic Sea and Bristol Channel), Belgium also obtained a derogation. Thus, both are not included in the monitoring programme. Setting up discard sampling programmes for this fishery is disproportionate compared to the added value to the international data collection. Moreover, it is of limited importance to the Belgian fisheries (8% of landings). The remaining fisheries such as Scottish seine (SSC), Boat dredge (DRB), trammel nets (GTR) and gill nets (GNS) were also not included because 1) they comprise less than 10% of the landings; 2) the number of vessels within these fleets is often too small to guarantee privacy of the collected data and/or 3) there is no space for taking observers on board. The two fleet segments (TBB_DEF_>221 kW and TBB_DEF_<=221 kW) are treated as two separate strata in the Belgian at sea sampling programme. Catch information (landings and discards are covered) is obtained through on-board observation. Four ILVO observers assure a sampling coverage of on average 1% of all fishing hours (approximately 40 trips on an annual basis). The sampling effort targets for one year are set at 8 trips for the TBB_DEF_<=221 kW fleet segment and 34 trips for the TBB_DEF_>221 kW fleet segment. This programme contributes to environmental targets D3.1, D3.2, D3.3, D3.4 and D1.4. (former programme ANSBE-D3-Commercial-fish-SP13 )
Fisheries Observer Programme: On commercial vessels, a sea-going observer collects data on species, numbers, length and weight of the caught fish. Samples are brought to the lab for individual analysis of length, weight, sex, maturity and age. The observer also documents recordings of certain bycatch species (protected fish, birds, turtles or mammals). Based on the selection criteria described by the Data Collection Framework (DCF), and considering the importance of the Belgian beam trawl fleet targeting demersal species (TBB_DEF), Belgium focusses on the collection of fishery-dependent data for this fleet (both fleet segments TBB_DEF_>221 kW and TBB_DEF_<=221 kW coastal vessels and euro cutters). For the beam trawl targeting crustaceans (TBB_CRU), representing 5% of the landings, Belgium has obtained a derogation in area IV (North Sea) and VIId (Eastern English Channel). For the bottom otter trawls (OTB) in VIIfg (Celtic Sea and Bristol Channel), Belgium also obtained a derogation. Thus, both are not included in the monitoring programme. Setting up discard sampling programmes for this fishery is disproportionate compared to the added value to the international data collection. Moreover, it is of limited importance to the Belgian fisheries (8% of landings). The remaining fisheries such as Scottish seine (SSC), Boat dredge (DRB), trammel nets (GTR) and gill nets (GNS) were also not included because 1) they comprise less than 10% of the landings; 2) the number of vessels within these fleets is often too small to guarantee privacy of the collected data and/or 3) there is no space for taking observers on board. The two fleet segments (TBB_DEF_>221 kW and TBB_DEF_<=221 kW) are treated as two separate strata in the Belgian at sea sampling programme. Catch information (landings and discards are covered) is obtained through on-board observation. Four ILVO observers assure a sampling coverage of on average 1% of all fishing hours (approximately 40 trips on an annual basis). The sampling effort targets for one year are set at 8 trips for the TBB_DEF_<=221 kW fleet segment and 34 trips for the TBB_DEF_>221 kW fleet segment. This programme contributes to environmental targets D3.1, D3.2, D3.3, D3.4 and D1.4. (former programme ANSBE-D3-Commercial-fish-SP13 )
Fisheries Observer Programme: On commercial vessels, a sea-going observer collects data on species, numbers, length and weight of the caught fish. Samples are brought to the lab for individual analysis of length, weight, sex, maturity and age. The observer also documents recordings of certain bycatch species (protected fish, birds, turtles or mammals). Based on the selection criteria described by the Data Collection Framework (DCF), and considering the importance of the Belgian beam trawl fleet targeting demersal species (TBB_DEF), Belgium focusses on the collection of fishery-dependent data for this fleet (both fleet segments TBB_DEF_>221 kW and TBB_DEF_<=221 kW coastal vessels and euro cutters). For the beam trawl targeting crustaceans (TBB_CRU), representing 5% of the landings, Belgium has obtained a derogation in area IV (North Sea) and VIId (Eastern English Channel). For the bottom otter trawls (OTB) in VIIfg (Celtic Sea and Bristol Channel), Belgium also obtained a derogation. Thus, both are not included in the monitoring programme. Setting up discard sampling programmes for this fishery is disproportionate compared to the added value to the international data collection. Moreover, it is of limited importance to the Belgian fisheries (8% of landings). The remaining fisheries such as Scottish seine (SSC), Boat dredge (DRB), trammel nets (GTR) and gill nets (GNS) were also not included because 1) they comprise less than 10% of the landings; 2) the number of vessels within these fleets is often too small to guarantee privacy of the collected data and/or 3) there is no space for taking observers on board. The two fleet segments (TBB_DEF_>221 kW and TBB_DEF_<=221 kW) are treated as two separate strata in the Belgian at sea sampling programme. Catch information (landings and discards are covered) is obtained through on-board observation. Four ILVO observers assure a sampling coverage of on average 1% of all fishing hours (approximately 40 trips on an annual basis). The sampling effort targets for one year are set at 8 trips for the TBB_DEF_<=221 kW fleet segment and 34 trips for the TBB_DEF_>221 kW fleet segment. This programme contributes to environmental targets D3.1, D3.2, D3.3, D3.4 and D1.4. (former programme ANSBE-D3-Commercial-fish-SP13 )
Fisheries Observer Programme: On commercial vessels, a sea-going observer collects data on species, numbers, length and weight of the caught fish. Samples are brought to the lab for individual analysis of length, weight, sex, maturity and age. The observer also documents recordings of certain bycatch species (protected fish, birds, turtles or mammals). Based on the selection criteria described by the Data Collection Framework (DCF), and considering the importance of the Belgian beam trawl fleet targeting demersal species (TBB_DEF), Belgium focusses on the collection of fishery-dependent data for this fleet (both fleet segments TBB_DEF_>221 kW and TBB_DEF_<=221 kW coastal vessels and euro cutters). For the beam trawl targeting crustaceans (TBB_CRU), representing 5% of the landings, Belgium has obtained a derogation in area IV (North Sea) and VIId (Eastern English Channel). For the bottom otter trawls (OTB) in VIIfg (Celtic Sea and Bristol Channel), Belgium also obtained a derogation. Thus, both are not included in the monitoring programme. Setting up discard sampling programmes for this fishery is disproportionate compared to the added value to the international data collection. Moreover, it is of limited importance to the Belgian fisheries (8% of landings). The remaining fisheries such as Scottish seine (SSC), Boat dredge (DRB), trammel nets (GTR) and gill nets (GNS) were also not included because 1) they comprise less than 10% of the landings; 2) the number of vessels within these fleets is often too small to guarantee privacy of the collected data and/or 3) there is no space for taking observers on board. The two fleet segments (TBB_DEF_>221 kW and TBB_DEF_<=221 kW) are treated as two separate strata in the Belgian at sea sampling programme. Catch information (landings and discards are covered) is obtained through on-board observation. Four ILVO observers assure a sampling coverage of on average 1% of all fishing hours (approximately 40 trips on an annual basis). The sampling effort targets for one year are set at 8 trips for the TBB_DEF_<=221 kW fleet segment and 34 trips for the TBB_DEF_>221 kW fleet segment. This programme contributes to environmental targets D3.1, D3.2, D3.3, D3.4 and D1.4. (former programme ANSBE-D3-Commercial-fish-SP13 )
Two types of data are collected: 1. North Sea Beam Trawl Survey (BTS) The Belgian offshore beam trawl survey with RV Belgica, collecting fisheries-independent data primarily for plaice (Pleuronectes platessa) and sole (Solea solea) in the North Sea (area IVb,c), started in 1992. The continuous time-series using a 4m-beam trawl as standard gear, started in 1993. The main objectives of the BTS are: • creation of fisheries-independent stock estimates for plaice (Pleuronectes platessa) and sole (Solea solea) in the sampled area • collection of data on all fish species for ecosystem purposes • collection of data on epibenthos species for ecosystem purposes 2. Demersal Young Fish Survey (DYFS) As part of the international Demersal Young Fish and Brown Shrimp Survey, an annual autumn (quarter 3) DYFS survey is carried out with RV Simon Stevin in the Belgian coastal waters by ILVO. The main objective of the DYFS is to collect data on the abundance and distribution of juvenile flatfish (primarily plaice and sole) and brown shrimp (Crangon crangon). Fish survey information needs to be collected in a standardized and fishery-independent way, to serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Since 1973, 33 fixed sampling stations have been fished in this way on an annual basis by ILVO, with a geographical match of the sampling stations with the main flatfish and brown shrimp nursery grounds along the Belgian coast. Following the Data Collection Framework (DCF), the DYFS is also an ecosystem survey. Belgium (ILVO) has been actively participating in the ICES Working Group on Beam Trawl Surveys (WGBEAM), where inshore (DYFS) and offshore (BTS) beam trawl surveys are coordinated and further standardisation is aimed for. For the North Sea, only the survey indices of the four countries listed are used in WGBEAM. This programme contributes to the environmental targets D3.1, D3.2, D3.3 and D1.4. (Former programme ANSBE-D1-4-Fish-SP3)
Two types of data are collected: 1. North Sea Beam Trawl Survey (BTS) The Belgian offshore beam trawl survey with RV Belgica, collecting fisheries-independent data primarily for plaice (Pleuronectes platessa) and sole (Solea solea) in the North Sea (area IVb,c), started in 1992. The continuous time-series using a 4m-beam trawl as standard gear, started in 1993. The main objectives of the BTS are: • creation of fisheries-independent stock estimates for plaice (Pleuronectes platessa) and sole (Solea solea) in the sampled area • collection of data on all fish species for ecosystem purposes • collection of data on epibenthos species for ecosystem purposes 2. Demersal Young Fish Survey (DYFS) As part of the international Demersal Young Fish and Brown Shrimp Survey, an annual autumn (quarter 3) DYFS survey is carried out with RV Simon Stevin in the Belgian coastal waters by ILVO. The main objective of the DYFS is to collect data on the abundance and distribution of juvenile flatfish (primarily plaice and sole) and brown shrimp (Crangon crangon). Fish survey information needs to be collected in a standardized and fishery-independent way, to serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Since 1973, 33 fixed sampling stations have been fished in this way on an annual basis by ILVO, with a geographical match of the sampling stations with the main flatfish and brown shrimp nursery grounds along the Belgian coast. Following the Data Collection Framework (DCF), the DYFS is also an ecosystem survey. Belgium (ILVO) has been actively participating in the ICES Working Group on Beam Trawl Surveys (WGBEAM), where inshore (DYFS) and offshore (BTS) beam trawl surveys are coordinated and further standardisation is aimed for. For the North Sea, only the survey indices of the four countries listed are used in WGBEAM. This programme contributes to the environmental targets D3.1, D3.2, D3.3 and D1.4. (Former programme ANSBE-D1-4-Fish-SP3)
Two types of data are collected: 1. North Sea Beam Trawl Survey (BTS) The Belgian offshore beam trawl survey with RV Belgica, collecting fisheries-independent data primarily for plaice (Pleuronectes platessa) and sole (Solea solea) in the North Sea (area IVb,c), started in 1992. The continuous time-series using a 4m-beam trawl as standard gear, started in 1993. The main objectives of the BTS are: • creation of fisheries-independent stock estimates for plaice (Pleuronectes platessa) and sole (Solea solea) in the sampled area • collection of data on all fish species for ecosystem purposes • collection of data on epibenthos species for ecosystem purposes 2. Demersal Young Fish Survey (DYFS) As part of the international Demersal Young Fish and Brown Shrimp Survey, an annual autumn (quarter 3) DYFS survey is carried out with RV Simon Stevin in the Belgian coastal waters by ILVO. The main objective of the DYFS is to collect data on the abundance and distribution of juvenile flatfish (primarily plaice and sole) and brown shrimp (Crangon crangon). Fish survey information needs to be collected in a standardized and fishery-independent way, to serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Since 1973, 33 fixed sampling stations have been fished in this way on an annual basis by ILVO, with a geographical match of the sampling stations with the main flatfish and brown shrimp nursery grounds along the Belgian coast. Following the Data Collection Framework (DCF), the DYFS is also an ecosystem survey. Belgium (ILVO) has been actively participating in the ICES Working Group on Beam Trawl Surveys (WGBEAM), where inshore (DYFS) and offshore (BTS) beam trawl surveys are coordinated and further standardisation is aimed for. For the North Sea, only the survey indices of the four countries listed are used in WGBEAM. This programme contributes to the environmental targets D3.1, D3.2, D3.3 and D1.4. (Former programme ANSBE-D1-4-Fish-SP3)
Two types of data are collected: 1. North Sea Beam Trawl Survey (BTS) The Belgian offshore beam trawl survey with RV Belgica, collecting fisheries-independent data primarily for plaice (Pleuronectes platessa) and sole (Solea solea) in the North Sea (area IVb,c), started in 1992. The continuous time-series using a 4m-beam trawl as standard gear, started in 1993. The main objectives of the BTS are: • creation of fisheries-independent stock estimates for plaice (Pleuronectes platessa) and sole (Solea solea) in the sampled area • collection of data on all fish species for ecosystem purposes • collection of data on epibenthos species for ecosystem purposes 2. Demersal Young Fish Survey (DYFS) As part of the international Demersal Young Fish and Brown Shrimp Survey, an annual autumn (quarter 3) DYFS survey is carried out with RV Simon Stevin in the Belgian coastal waters by ILVO. The main objective of the DYFS is to collect data on the abundance and distribution of juvenile flatfish (primarily plaice and sole) and brown shrimp (Crangon crangon). Fish survey information needs to be collected in a standardized and fishery-independent way, to serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Since 1973, 33 fixed sampling stations have been fished in this way on an annual basis by ILVO, with a geographical match of the sampling stations with the main flatfish and brown shrimp nursery grounds along the Belgian coast. Following the Data Collection Framework (DCF), the DYFS is also an ecosystem survey. Belgium (ILVO) has been actively participating in the ICES Working Group on Beam Trawl Surveys (WGBEAM), where inshore (DYFS) and offshore (BTS) beam trawl surveys are coordinated and further standardisation is aimed for. For the North Sea, only the survey indices of the four countries listed are used in WGBEAM. This programme contributes to the environmental targets D3.1, D3.2, D3.3 and D1.4. (Former programme ANSBE-D1-4-Fish-SP3)
Monitoring purpose
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
Other policies and conventions
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
Regional cooperation - coordinating body
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
Regional cooperation - countries involved
DE,DK,ES,FR,IE,NL,PT,UK
DE,DK,ES,FR,IE,NL,PT,UK
DE,DK,ES,FR,IE,NL,PT,UK
DE,DK,ES,FR,IE,NL,PT,UK
DE,DK,ES,FR,IE,NL,PT,UK
DE,DK,ES,FR,IE,NL,PT,UK
DE,DK,ES,FR,IE,NL,PT,UK
BE,DE,NL,UK
BE,DE,NL,UK
BE,DE,NL,UK
BE,DE,NL,UK
Regional cooperation - implementation level
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Monitoring details
The primary sampling unit (PSU) in the Belgian at sea sampling programme is vessel x trip (as a proxy for trip). A vessel x trip (PSU) for the TBB_DEF_>221 kW fleet segment is selected ad hoc or standard quota sampling is conducted (non-probability-based sampling). The vessels that are willing to take observers onboard and those that are logistically suited, are included in the vessel list, that currently contains ± 15 vessels over which the sampling will be spread. ILVO introduced 2 types of sampling: 1. Ad hoc sampling: for those strata with a lower sampling coverage (based on previous years) 2. Quota sampling: sampling effort is proportionally to the fleet effort (based on previous year) A vessel x trip (PSU) for the TBB_DEF_<=221 kW fleet segment is selected ad hoc. More than half of TBB_DEF vessels with a capacity <=221 kW flying the Belgian flag are regularly fishing for shrimp (TBB_CRU). Belgium has a derogation for sampling the TBB_CRU métier until the end of 2021. The TBB_DEF_<=221 kW vessel list proved too small to ensure random PSU selection. Therefore, ad hoc sampling of 2 euro cutters and 2 coastal vessels is carried out. The observer coordinator keeps track of the vessels in the vessel list but ILVO considers collecting non-responses and refusals on PSU (trip) level not relevant. Every other haul is sampled by an observer. For the TBB_DEF_<=221 kW fleet segment, the aim is to sample all hauls during the short trips of the coastal vessels. The crew sorts the marketable fish from the conveyor belt. In the meantime, the observer is sampling the discarded fraction of the catch by sorting all commercially important species. The total weight per species in each haul is determined and lengths are measured. When a species is extremely abundant, a smaller representative subsample (TSU) is measured. The marketable part of the catch (landings) is sampled later on in the same way as the discarded part of the catch. For selected species (depending on the area), otoliths from minimum 3 fish per cm-size class per species per area, are collected (except for 1 fish per cm-size class for cod) for age estimations. Otoliths are collected throughout the whole trip (several hauls) until the quota for otoliths is achieved. For the discarded part of the catch, otoliths are being removed on board. For the retained part (landings) of the catch, the fish are purchased. Coordination takes place within the Regional Coordination Groups (RCG NA/RCG NSE).
The primary sampling unit (PSU) in the Belgian at sea sampling programme is vessel x trip (as a proxy for trip). A vessel x trip (PSU) for the TBB_DEF_>221 kW fleet segment is selected ad hoc or standard quota sampling is conducted (non-probability-based sampling). The vessels that are willing to take observers onboard and those that are logistically suited, are included in the vessel list, that currently contains ± 15 vessels over which the sampling will be spread. ILVO introduced 2 types of sampling: 1. Ad hoc sampling: for those strata with a lower sampling coverage (based on previous years) 2. Quota sampling: sampling effort is proportionally to the fleet effort (based on previous year) A vessel x trip (PSU) for the TBB_DEF_<=221 kW fleet segment is selected ad hoc. More than half of TBB_DEF vessels with a capacity <=221 kW flying the Belgian flag are regularly fishing for shrimp (TBB_CRU). Belgium has a derogation for sampling the TBB_CRU métier until the end of 2021. The TBB_DEF_<=221 kW vessel list proved too small to ensure random PSU selection. Therefore, ad hoc sampling of 2 euro cutters and 2 coastal vessels is carried out. The observer coordinator keeps track of the vessels in the vessel list but ILVO considers collecting non-responses and refusals on PSU (trip) level not relevant. Every other haul is sampled by an observer. For the TBB_DEF_<=221 kW fleet segment, the aim is to sample all hauls during the short trips of the coastal vessels. The crew sorts the marketable fish from the conveyor belt. In the meantime, the observer is sampling the discarded fraction of the catch by sorting all commercially important species. The total weight per species in each haul is determined and lengths are measured. When a species is extremely abundant, a smaller representative subsample (TSU) is measured. The marketable part of the catch (landings) is sampled later on in the same way as the discarded part of the catch. For selected species (depending on the area), otoliths from minimum 3 fish per cm-size class per species per area, are collected (except for 1 fish per cm-size class for cod) for age estimations. Otoliths are collected throughout the whole trip (several hauls) until the quota for otoliths is achieved. For the discarded part of the catch, otoliths are being removed on board. For the retained part (landings) of the catch, the fish are purchased. Coordination takes place within the Regional Coordination Groups (RCG NA/RCG NSE).
The primary sampling unit (PSU) in the Belgian at sea sampling programme is vessel x trip (as a proxy for trip). A vessel x trip (PSU) for the TBB_DEF_>221 kW fleet segment is selected ad hoc or standard quota sampling is conducted (non-probability-based sampling). The vessels that are willing to take observers onboard and those that are logistically suited, are included in the vessel list, that currently contains ± 15 vessels over which the sampling will be spread. ILVO introduced 2 types of sampling: 1. Ad hoc sampling: for those strata with a lower sampling coverage (based on previous years) 2. Quota sampling: sampling effort is proportionally to the fleet effort (based on previous year) A vessel x trip (PSU) for the TBB_DEF_<=221 kW fleet segment is selected ad hoc. More than half of TBB_DEF vessels with a capacity <=221 kW flying the Belgian flag are regularly fishing for shrimp (TBB_CRU). Belgium has a derogation for sampling the TBB_CRU métier until the end of 2021. The TBB_DEF_<=221 kW vessel list proved too small to ensure random PSU selection. Therefore, ad hoc sampling of 2 euro cutters and 2 coastal vessels is carried out. The observer coordinator keeps track of the vessels in the vessel list but ILVO considers collecting non-responses and refusals on PSU (trip) level not relevant. Every other haul is sampled by an observer. For the TBB_DEF_<=221 kW fleet segment, the aim is to sample all hauls during the short trips of the coastal vessels. The crew sorts the marketable fish from the conveyor belt. In the meantime, the observer is sampling the discarded fraction of the catch by sorting all commercially important species. The total weight per species in each haul is determined and lengths are measured. When a species is extremely abundant, a smaller representative subsample (TSU) is measured. The marketable part of the catch (landings) is sampled later on in the same way as the discarded part of the catch. For selected species (depending on the area), otoliths from minimum 3 fish per cm-size class per species per area, are collected (except for 1 fish per cm-size class for cod) for age estimations. Otoliths are collected throughout the whole trip (several hauls) until the quota for otoliths is achieved. For the discarded part of the catch, otoliths are being removed on board. For the retained part (landings) of the catch, the fish are purchased. Coordination takes place within the Regional Coordination Groups (RCG NA/RCG NSE).
The primary sampling unit (PSU) in the Belgian at sea sampling programme is vessel x trip (as a proxy for trip). A vessel x trip (PSU) for the TBB_DEF_>221 kW fleet segment is selected ad hoc or standard quota sampling is conducted (non-probability-based sampling). The vessels that are willing to take observers onboard and those that are logistically suited, are included in the vessel list, that currently contains ± 15 vessels over which the sampling will be spread. ILVO introduced 2 types of sampling: 1. Ad hoc sampling: for those strata with a lower sampling coverage (based on previous years) 2. Quota sampling: sampling effort is proportionally to the fleet effort (based on previous year) A vessel x trip (PSU) for the TBB_DEF_<=221 kW fleet segment is selected ad hoc. More than half of TBB_DEF vessels with a capacity <=221 kW flying the Belgian flag are regularly fishing for shrimp (TBB_CRU). Belgium has a derogation for sampling the TBB_CRU métier until the end of 2021. The TBB_DEF_<=221 kW vessel list proved too small to ensure random PSU selection. Therefore, ad hoc sampling of 2 euro cutters and 2 coastal vessels is carried out. The observer coordinator keeps track of the vessels in the vessel list but ILVO considers collecting non-responses and refusals on PSU (trip) level not relevant. Every other haul is sampled by an observer. For the TBB_DEF_<=221 kW fleet segment, the aim is to sample all hauls during the short trips of the coastal vessels. The crew sorts the marketable fish from the conveyor belt. In the meantime, the observer is sampling the discarded fraction of the catch by sorting all commercially important species. The total weight per species in each haul is determined and lengths are measured. When a species is extremely abundant, a smaller representative subsample (TSU) is measured. The marketable part of the catch (landings) is sampled later on in the same way as the discarded part of the catch. For selected species (depending on the area), otoliths from minimum 3 fish per cm-size class per species per area, are collected (except for 1 fish per cm-size class for cod) for age estimations. Otoliths are collected throughout the whole trip (several hauls) until the quota for otoliths is achieved. For the discarded part of the catch, otoliths are being removed on board. For the retained part (landings) of the catch, the fish are purchased. Coordination takes place within the Regional Coordination Groups (RCG NA/RCG NSE).
The primary sampling unit (PSU) in the Belgian at sea sampling programme is vessel x trip (as a proxy for trip). A vessel x trip (PSU) for the TBB_DEF_>221 kW fleet segment is selected ad hoc or standard quota sampling is conducted (non-probability-based sampling). The vessels that are willing to take observers onboard and those that are logistically suited, are included in the vessel list, that currently contains ± 15 vessels over which the sampling will be spread. ILVO introduced 2 types of sampling: 1. Ad hoc sampling: for those strata with a lower sampling coverage (based on previous years) 2. Quota sampling: sampling effort is proportionally to the fleet effort (based on previous year) A vessel x trip (PSU) for the TBB_DEF_<=221 kW fleet segment is selected ad hoc. More than half of TBB_DEF vessels with a capacity <=221 kW flying the Belgian flag are regularly fishing for shrimp (TBB_CRU). Belgium has a derogation for sampling the TBB_CRU métier until the end of 2021. The TBB_DEF_<=221 kW vessel list proved too small to ensure random PSU selection. Therefore, ad hoc sampling of 2 euro cutters and 2 coastal vessels is carried out. The observer coordinator keeps track of the vessels in the vessel list but ILVO considers collecting non-responses and refusals on PSU (trip) level not relevant. Every other haul is sampled by an observer. For the TBB_DEF_<=221 kW fleet segment, the aim is to sample all hauls during the short trips of the coastal vessels. The crew sorts the marketable fish from the conveyor belt. In the meantime, the observer is sampling the discarded fraction of the catch by sorting all commercially important species. The total weight per species in each haul is determined and lengths are measured. When a species is extremely abundant, a smaller representative subsample (TSU) is measured. The marketable part of the catch (landings) is sampled later on in the same way as the discarded part of the catch. For selected species (depending on the area), otoliths from minimum 3 fish per cm-size class per species per area, are collected (except for 1 fish per cm-size class for cod) for age estimations. Otoliths are collected throughout the whole trip (several hauls) until the quota for otoliths is achieved. For the discarded part of the catch, otoliths are being removed on board. For the retained part (landings) of the catch, the fish are purchased. Coordination takes place within the Regional Coordination Groups (RCG NA/RCG NSE).
The primary sampling unit (PSU) in the Belgian at sea sampling programme is vessel x trip (as a proxy for trip). A vessel x trip (PSU) for the TBB_DEF_>221 kW fleet segment is selected ad hoc or standard quota sampling is conducted (non-probability-based sampling). The vessels that are willing to take observers onboard and those that are logistically suited, are included in the vessel list, that currently contains ± 15 vessels over which the sampling will be spread. ILVO introduced 2 types of sampling: 1. Ad hoc sampling: for those strata with a lower sampling coverage (based on previous years) 2. Quota sampling: sampling effort is proportionally to the fleet effort (based on previous year) A vessel x trip (PSU) for the TBB_DEF_<=221 kW fleet segment is selected ad hoc. More than half of TBB_DEF vessels with a capacity <=221 kW flying the Belgian flag are regularly fishing for shrimp (TBB_CRU). Belgium has a derogation for sampling the TBB_CRU métier until the end of 2021. The TBB_DEF_<=221 kW vessel list proved too small to ensure random PSU selection. Therefore, ad hoc sampling of 2 euro cutters and 2 coastal vessels is carried out. The observer coordinator keeps track of the vessels in the vessel list but ILVO considers collecting non-responses and refusals on PSU (trip) level not relevant. Every other haul is sampled by an observer. For the TBB_DEF_<=221 kW fleet segment, the aim is to sample all hauls during the short trips of the coastal vessels. The crew sorts the marketable fish from the conveyor belt. In the meantime, the observer is sampling the discarded fraction of the catch by sorting all commercially important species. The total weight per species in each haul is determined and lengths are measured. When a species is extremely abundant, a smaller representative subsample (TSU) is measured. The marketable part of the catch (landings) is sampled later on in the same way as the discarded part of the catch. For selected species (depending on the area), otoliths from minimum 3 fish per cm-size class per species per area, are collected (except for 1 fish per cm-size class for cod) for age estimations. Otoliths are collected throughout the whole trip (several hauls) until the quota for otoliths is achieved. For the discarded part of the catch, otoliths are being removed on board. For the retained part (landings) of the catch, the fish are purchased. Coordination takes place within the Regional Coordination Groups (RCG NA/RCG NSE).
The primary sampling unit (PSU) in the Belgian at sea sampling programme is vessel x trip (as a proxy for trip). A vessel x trip (PSU) for the TBB_DEF_>221 kW fleet segment is selected ad hoc or standard quota sampling is conducted (non-probability-based sampling). The vessels that are willing to take observers onboard and those that are logistically suited, are included in the vessel list, that currently contains ± 15 vessels over which the sampling will be spread. ILVO introduced 2 types of sampling: 1. Ad hoc sampling: for those strata with a lower sampling coverage (based on previous years) 2. Quota sampling: sampling effort is proportionally to the fleet effort (based on previous year) A vessel x trip (PSU) for the TBB_DEF_<=221 kW fleet segment is selected ad hoc. More than half of TBB_DEF vessels with a capacity <=221 kW flying the Belgian flag are regularly fishing for shrimp (TBB_CRU). Belgium has a derogation for sampling the TBB_CRU métier until the end of 2021. The TBB_DEF_<=221 kW vessel list proved too small to ensure random PSU selection. Therefore, ad hoc sampling of 2 euro cutters and 2 coastal vessels is carried out. The observer coordinator keeps track of the vessels in the vessel list but ILVO considers collecting non-responses and refusals on PSU (trip) level not relevant. Every other haul is sampled by an observer. For the TBB_DEF_<=221 kW fleet segment, the aim is to sample all hauls during the short trips of the coastal vessels. The crew sorts the marketable fish from the conveyor belt. In the meantime, the observer is sampling the discarded fraction of the catch by sorting all commercially important species. The total weight per species in each haul is determined and lengths are measured. When a species is extremely abundant, a smaller representative subsample (TSU) is measured. The marketable part of the catch (landings) is sampled later on in the same way as the discarded part of the catch. For selected species (depending on the area), otoliths from minimum 3 fish per cm-size class per species per area, are collected (except for 1 fish per cm-size class for cod) for age estimations. Otoliths are collected throughout the whole trip (several hauls) until the quota for otoliths is achieved. For the discarded part of the catch, otoliths are being removed on board. For the retained part (landings) of the catch, the fish are purchased. Coordination takes place within the Regional Coordination Groups (RCG NA/RCG NSE).
1. BTS During the BTS 62 fixed stations are fished for 30 min at 4 knots using a beam trawl as standard gear (beam length 4 m, cod-end mesh size 40 mm). Although the target species are plaice and sole, all fish and commercially important cephalopods and crustaceans are sorted, weighed and measured since 2010. Since 2009, a subsample of the catch is taken of which all epibenthic species are recorded in numbers and sample weight. The data collected during the BTS are used in analytical population studies of several species/stocks, mainly serving as tuning indices in the stock assessments leading to the fishing quota. Additionally, several other investigations are planned, such as (a) the construction of "age-length-keys" for a number of commercially important flatfish, and (b) documenting distribution and abundance of all commercial and non-commercial (bycatch) invertebrate species. 2. DYFS All 33 DYFS sampling stations are fished for approximately 30 min, with a standard shrimp beam trawl (beam length 6 m; cod-end mesh size 22 mm, no tickler chains), at 3 knots against tide. Several fish species (cod, whiting, plaice, flounder, dab, sole, brill and turbot) are hand-picked from the catches, sorted by species, weighed and measured in mm (by the in-house developed SmartFish measuring board). From 2009 onwards, the species list was extended to cover a larger range of commercial fish species (e.g. including lesser spotted dogfish, gurnards, lemon sole, horse mackerel, etc.). In this way, a total of 18 species are documented. From 2018 onwards, the species list has been extended with all elasmobranch species that are weighed and measured (by sex). The brown shrimp from the catches are first sorted into a ‘small’ and ‘large’ fraction by means of a rotating shrimp riddle (same type used on commercial shrimp trawlers). From each of these two fractions, 1-2 liter samples are taken (depending on the amount of shrimp and other organisms in the fractions). Samples are further sub-sampled in the lab to approximately 250 shrimps, which are then measured in mm using an in-house developed system.
1. BTS During the BTS 62 fixed stations are fished for 30 min at 4 knots using a beam trawl as standard gear (beam length 4 m, cod-end mesh size 40 mm). Although the target species are plaice and sole, all fish and commercially important cephalopods and crustaceans are sorted, weighed and measured since 2010. Since 2009, a subsample of the catch is taken of which all epibenthic species are recorded in numbers and sample weight. The data collected during the BTS are used in analytical population studies of several species/stocks, mainly serving as tuning indices in the stock assessments leading to the fishing quota. Additionally, several other investigations are planned, such as (a) the construction of "age-length-keys" for a number of commercially important flatfish, and (b) documenting distribution and abundance of all commercial and non-commercial (bycatch) invertebrate species. 2. DYFS All 33 DYFS sampling stations are fished for approximately 30 min, with a standard shrimp beam trawl (beam length 6 m; cod-end mesh size 22 mm, no tickler chains), at 3 knots against tide. Several fish species (cod, whiting, plaice, flounder, dab, sole, brill and turbot) are hand-picked from the catches, sorted by species, weighed and measured in mm (by the in-house developed SmartFish measuring board). From 2009 onwards, the species list was extended to cover a larger range of commercial fish species (e.g. including lesser spotted dogfish, gurnards, lemon sole, horse mackerel, etc.). In this way, a total of 18 species are documented. From 2018 onwards, the species list has been extended with all elasmobranch species that are weighed and measured (by sex). The brown shrimp from the catches are first sorted into a ‘small’ and ‘large’ fraction by means of a rotating shrimp riddle (same type used on commercial shrimp trawlers). From each of these two fractions, 1-2 liter samples are taken (depending on the amount of shrimp and other organisms in the fractions). Samples are further sub-sampled in the lab to approximately 250 shrimps, which are then measured in mm using an in-house developed system.
1. BTS During the BTS 62 fixed stations are fished for 30 min at 4 knots using a beam trawl as standard gear (beam length 4 m, cod-end mesh size 40 mm). Although the target species are plaice and sole, all fish and commercially important cephalopods and crustaceans are sorted, weighed and measured since 2010. Since 2009, a subsample of the catch is taken of which all epibenthic species are recorded in numbers and sample weight. The data collected during the BTS are used in analytical population studies of several species/stocks, mainly serving as tuning indices in the stock assessments leading to the fishing quota. Additionally, several other investigations are planned, such as (a) the construction of "age-length-keys" for a number of commercially important flatfish, and (b) documenting distribution and abundance of all commercial and non-commercial (bycatch) invertebrate species. 2. DYFS All 33 DYFS sampling stations are fished for approximately 30 min, with a standard shrimp beam trawl (beam length 6 m; cod-end mesh size 22 mm, no tickler chains), at 3 knots against tide. Several fish species (cod, whiting, plaice, flounder, dab, sole, brill and turbot) are hand-picked from the catches, sorted by species, weighed and measured in mm (by the in-house developed SmartFish measuring board). From 2009 onwards, the species list was extended to cover a larger range of commercial fish species (e.g. including lesser spotted dogfish, gurnards, lemon sole, horse mackerel, etc.). In this way, a total of 18 species are documented. From 2018 onwards, the species list has been extended with all elasmobranch species that are weighed and measured (by sex). The brown shrimp from the catches are first sorted into a ‘small’ and ‘large’ fraction by means of a rotating shrimp riddle (same type used on commercial shrimp trawlers). From each of these two fractions, 1-2 liter samples are taken (depending on the amount of shrimp and other organisms in the fractions). Samples are further sub-sampled in the lab to approximately 250 shrimps, which are then measured in mm using an in-house developed system.
1. BTS During the BTS 62 fixed stations are fished for 30 min at 4 knots using a beam trawl as standard gear (beam length 4 m, cod-end mesh size 40 mm). Although the target species are plaice and sole, all fish and commercially important cephalopods and crustaceans are sorted, weighed and measured since 2010. Since 2009, a subsample of the catch is taken of which all epibenthic species are recorded in numbers and sample weight. The data collected during the BTS are used in analytical population studies of several species/stocks, mainly serving as tuning indices in the stock assessments leading to the fishing quota. Additionally, several other investigations are planned, such as (a) the construction of "age-length-keys" for a number of commercially important flatfish, and (b) documenting distribution and abundance of all commercial and non-commercial (bycatch) invertebrate species. 2. DYFS All 33 DYFS sampling stations are fished for approximately 30 min, with a standard shrimp beam trawl (beam length 6 m; cod-end mesh size 22 mm, no tickler chains), at 3 knots against tide. Several fish species (cod, whiting, plaice, flounder, dab, sole, brill and turbot) are hand-picked from the catches, sorted by species, weighed and measured in mm (by the in-house developed SmartFish measuring board). From 2009 onwards, the species list was extended to cover a larger range of commercial fish species (e.g. including lesser spotted dogfish, gurnards, lemon sole, horse mackerel, etc.). In this way, a total of 18 species are documented. From 2018 onwards, the species list has been extended with all elasmobranch species that are weighed and measured (by sex). The brown shrimp from the catches are first sorted into a ‘small’ and ‘large’ fraction by means of a rotating shrimp riddle (same type used on commercial shrimp trawlers). From each of these two fractions, 1-2 liter samples are taken (depending on the amount of shrimp and other organisms in the fractions). Samples are further sub-sampled in the lab to approximately 250 shrimps, which are then measured in mm using an in-house developed system.
Features
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Demersal shelf fish
Demersal shelf fish
Demersal shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Demersal shelf fish
Demersal shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Demersal shelf fish
Demersal shelf fish
Demersal shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Demersal shelf fish
Demersal shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Demersal shelf fish
Demersal shelf fish
Demersal shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Demersal shelf fish
Demersal shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Demersal shelf fish
Demersal shelf fish
Demersal shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Demersal shelf fish
Demersal shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Elements
  • Demersal fish community
  • Demersal fish community
  • Demersal fish community
  • Demersal fish community
  • Demersal fish community
  • Demersal fish community
  • Demersal fish community
  • Demersal fish community
  • Demersal fish community
  • Demersal fish community
GES criteria
D1C1
D1C2
D1C3
D3C1
D3C2
D3C3
D1C2
D1C3
D3C2
D3C3
Parameters
  • Mortality (weight/volume; number of individuals)
  • Abundance (number of individuals)
  • Biomass
  • Other
  • Age distribution
  • Length
  • Sex distribution
  • Mortality (weight/volume; number of individuals)
  • Mortality rate
  • Abundance (number of individuals)
  • Biomass of Spawning Stock (SSB)
  • Length
  • Size distribution
  • Abundance (number of individuals)
  • Biomass
  • Other
  • Age distribution
  • Length
  • Sex distribution
  • Abundance (number of individuals)
  • Biomass of Spawning Stock (SSB)
  • Length
  • Size distribution
Parameter Other
species composition
ag
species composition
Spatial scope
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
Marine reporting units
  • L2.2.5
  • L2.2.5
  • L2.2.5
  • L2.2.5
  • L2.2.5
  • L2.2.5
  • L2.2.5
  • L2.2.5
  • L2.2.5
  • L2.2.5
  • L2.2.5
Temporal scope (start date - end date)
1973-9999
1973-9999
1973-9999
1973-9999
1973-9999
1973-9999
1973-9999
1973-9999
1973-9999
1973-9999
1973-9999
Monitoring frequency
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Monitoring type
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
Monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
Monitoring method other
The protocol for the observer-at-sea programme can be found on smartfisheries.be (http://193.190.112.136/Portals/0/Publicaties/Protocol%20for%20at%20sea%20sampling%20programme%20ILVO%20-%202019.pdf?ver=2019-05-24-112532-673) All the at sea sampling data (metadata and all biological data) are recorded with the electronic measuring board (developed by ILVO) and stored in a national database called ‘SmartFish’.
The protocol for the observer-at-sea programme can be found on smartfisheries.be (http://193.190.112.136/Portals/0/Publicaties/Protocol%20for%20at%20sea%20sampling%20programme%20ILVO%20-%202019.pdf?ver=2019-05-24-112532-673) All the at sea sampling data (metadata and all biological data) are recorded with the electronic measuring board (developed by ILVO) and stored in a national database called ‘SmartFish’.
The protocol for the observer-at-sea programme can be found on smartfisheries.be (http://193.190.112.136/Portals/0/Publicaties/Protocol%20for%20at%20sea%20sampling%20programme%20ILVO%20-%202019.pdf?ver=2019-05-24-112532-673) All the at sea sampling data (metadata and all biological data) are recorded with the electronic measuring board (developed by ILVO) and stored in a national database called ‘SmartFish’.
The protocol for the observer-at-sea programme can be found on smartfisheries.be (http://193.190.112.136/Portals/0/Publicaties/Protocol%20for%20at%20sea%20sampling%20programme%20ILVO%20-%202019.pdf?ver=2019-05-24-112532-673) All the at sea sampling data (metadata and all biological data) are recorded with the electronic measuring board (developed by ILVO) and stored in a national database called ‘SmartFish’.
The protocol for the observer-at-sea programme can be found on smartfisheries.be (http://193.190.112.136/Portals/0/Publicaties/Protocol%20for%20at%20sea%20sampling%20programme%20ILVO%20-%202019.pdf?ver=2019-05-24-112532-673) All the at sea sampling data (metadata and all biological data) are recorded with the electronic measuring board (developed by ILVO) and stored in a national database called ‘SmartFish’.
The protocol for the observer-at-sea programme can be found on smartfisheries.be (http://193.190.112.136/Portals/0/Publicaties/Protocol%20for%20at%20sea%20sampling%20programme%20ILVO%20-%202019.pdf?ver=2019-05-24-112532-673) All the at sea sampling data (metadata and all biological data) are recorded with the electronic measuring board (developed by ILVO) and stored in a national database called ‘SmartFish’.
The protocol for the observer-at-sea programme can be found on smartfisheries.be (http://193.190.112.136/Portals/0/Publicaties/Protocol%20for%20at%20sea%20sampling%20programme%20ILVO%20-%202019.pdf?ver=2019-05-24-112532-673) All the at sea sampling data (metadata and all biological data) are recorded with the electronic measuring board (developed by ILVO) and stored in a national database called ‘SmartFish’.
Manual for the offshore Beam Trawl Surveys (Sisp-14) The North Sea Beam Trawl survey (BTS) methods are described in the Manual for the Offshore Beam Trawl Surveys (ICES. 2019. Manual for the Offshore Beam Trawl Surveys, Version 3.4, April 2019, Working Group on Beam Trawl Surveys. 54pp. http://doi.org/10.17895/ices.pub.5353). The methods for the Demersal Young Fish Survey (DYFS) are not yet available. During the WGBEAM meeting in 2015, a draft manual of this inshore survey was initiated and discussed. The working group aims to finalise the manual during WGBEAM meetings in the period 2020-2022.
Manual for the offshore Beam Trawl Surveys (Sisp-14) The North Sea Beam Trawl survey (BTS) methods are described in the Manual for the Offshore Beam Trawl Surveys (ICES. 2019. Manual for the Offshore Beam Trawl Surveys, Version 3.4, April 2019, Working Group on Beam Trawl Surveys. 54pp. http://doi.org/10.17895/ices.pub.5353). The methods for the Demersal Young Fish Survey (DYFS) are not yet available. During the WGBEAM meeting in 2015, a draft manual of this inshore survey was initiated and discussed. The working group aims to finalise the manual during WGBEAM meetings in the period 2020-2022.
Manual for the offshore Beam Trawl Surveys (Sisp-14) The North Sea Beam Trawl survey (BTS) methods are described in the Manual for the Offshore Beam Trawl Surveys (ICES. 2019. Manual for the Offshore Beam Trawl Surveys, Version 3.4, April 2019, Working Group on Beam Trawl Surveys. 54pp. http://doi.org/10.17895/ices.pub.5353). The methods for the Demersal Young Fish Survey (DYFS) are not yet available. During the WGBEAM meeting in 2015, a draft manual of this inshore survey was initiated and discussed. The working group aims to finalise the manual during WGBEAM meetings in the period 2020-2022.
Manual for the offshore Beam Trawl Surveys (Sisp-14) The North Sea Beam Trawl survey (BTS) methods are described in the Manual for the Offshore Beam Trawl Surveys (ICES. 2019. Manual for the Offshore Beam Trawl Surveys, Version 3.4, April 2019, Working Group on Beam Trawl Surveys. 54pp. http://doi.org/10.17895/ices.pub.5353). The methods for the Demersal Young Fish Survey (DYFS) are not yet available. During the WGBEAM meeting in 2015, a draft manual of this inshore survey was initiated and discussed. The working group aims to finalise the manual during WGBEAM meetings in the period 2020-2022.
Quality control
ISISO17025 An own developed national standard, approved by regional coordination and EC, Real and Delayed Validation For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used.
ISISO17025 An own developed national standard, approved by regional coordination and EC, Real and Delayed Validation For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used.
ISISO17025 An own developed national standard, approved by regional coordination and EC, Real and Delayed Validation For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used.
ISISO17025 An own developed national standard, approved by regional coordination and EC, Real and Delayed Validation For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used.
ISISO17025 An own developed national standard, approved by regional coordination and EC, Real and Delayed Validation For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used.
ISISO17025 An own developed national standard, approved by regional coordination and EC, Real and Delayed Validation For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used.
ISISO17025 An own developed national standard, approved by regional coordination and EC, Real and Delayed Validation For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used.
ISO17025 A national developed quality control standard (during and after the survey).
ISO17025 A national developed quality control standard (during and after the survey).
ISO17025 A national developed quality control standard (during and after the survey).
ISO17025 A national developed quality control standard (during and after the survey).
Data management
Data (trip, haul, samples) is stored at ILVO in the in-house database ‘Smartfish'. On a yearly basis, aggregated data products are provided to ICES for use in stock assessments. For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used. The data products serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Outcomes are the scientific advice sheets that can be consulted on the ICES website (https://www.ices.dk/community/advisory-process/Pages/Latest-Advice.aspx).
Data (trip, haul, samples) is stored at ILVO in the in-house database ‘Smartfish'. On a yearly basis, aggregated data products are provided to ICES for use in stock assessments. For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used. The data products serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Outcomes are the scientific advice sheets that can be consulted on the ICES website (https://www.ices.dk/community/advisory-process/Pages/Latest-Advice.aspx).
Data (trip, haul, samples) is stored at ILVO in the in-house database ‘Smartfish'. On a yearly basis, aggregated data products are provided to ICES for use in stock assessments. For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used. The data products serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Outcomes are the scientific advice sheets that can be consulted on the ICES website (https://www.ices.dk/community/advisory-process/Pages/Latest-Advice.aspx).
Data (trip, haul, samples) is stored at ILVO in the in-house database ‘Smartfish'. On a yearly basis, aggregated data products are provided to ICES for use in stock assessments. For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used. The data products serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Outcomes are the scientific advice sheets that can be consulted on the ICES website (https://www.ices.dk/community/advisory-process/Pages/Latest-Advice.aspx).
Data (trip, haul, samples) is stored at ILVO in the in-house database ‘Smartfish'. On a yearly basis, aggregated data products are provided to ICES for use in stock assessments. For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used. The data products serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Outcomes are the scientific advice sheets that can be consulted on the ICES website (https://www.ices.dk/community/advisory-process/Pages/Latest-Advice.aspx).
Data (trip, haul, samples) is stored at ILVO in the in-house database ‘Smartfish'. On a yearly basis, aggregated data products are provided to ICES for use in stock assessments. For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used. The data products serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Outcomes are the scientific advice sheets that can be consulted on the ICES website (https://www.ices.dk/community/advisory-process/Pages/Latest-Advice.aspx).
Data (trip, haul, samples) is stored at ILVO in the in-house database ‘Smartfish'. On a yearly basis, aggregated data products are provided to ICES for use in stock assessments. For quality assurance and analyses (e.g. raising) of the catch data, integrated checks in Smartfish, powerBI desktop and several R scripts (o.a. COST packages) are used. The data products serve as input data when running models to make prognoses for the fishing opportunities in the following years and calculating the fishing quota. Outcomes are the scientific advice sheets that can be consulted on the ICES website (https://www.ices.dk/community/advisory-process/Pages/Latest-Advice.aspx).
Indices of the abundance and biomass of adult flatfishes (mainly plaice and sole) are calculated by means of stratified tows in the southern and central North Sea. The results are incorporated in the survey database DATRAS, the databases of trawl surveys of ICES (www.datras.ices.dk). Currently, all Belgian survey data are stored at ILVO. The most recent data is stored in the national database of Smartfish. The data is expected to be uploaded to DATRAS on a yearly basis. The Belgian BTS data (2004-2019) and DYFS data (2011-2019) are already available in DATRAS. The historical DYFS- data (prior to 2011) and BTS data (1992-2003) are being prepared for uploading to DATRAS. Latest reports can be found on the website of WGBEAM (https://www.ices.dk/community/groups/Pages/WGBEAM.aspx), and in the case of the BTS on the RV BELGICA website ( https://odnature.naturalsciences.be/belgica/nl/campaign/1712) or for the DYFS on the MIDAS website (http://www.vliz.be/vmdcdata/midas/cruise.php?selectedcamp=103&showcamp=1).
Indices of the abundance and biomass of adult flatfishes (mainly plaice and sole) are calculated by means of stratified tows in the southern and central North Sea. The results are incorporated in the survey database DATRAS, the databases of trawl surveys of ICES (www.datras.ices.dk). Currently, all Belgian survey data are stored at ILVO. The most recent data is stored in the national database of Smartfish. The data is expected to be uploaded to DATRAS on a yearly basis. The Belgian BTS data (2004-2019) and DYFS data (2011-2019) are already available in DATRAS. The historical DYFS- data (prior to 2011) and BTS data (1992-2003) are being prepared for uploading to DATRAS. Latest reports can be found on the website of WGBEAM (https://www.ices.dk/community/groups/Pages/WGBEAM.aspx), and in the case of the BTS on the RV BELGICA website ( https://odnature.naturalsciences.be/belgica/nl/campaign/1712) or for the DYFS on the MIDAS website (http://www.vliz.be/vmdcdata/midas/cruise.php?selectedcamp=103&showcamp=1).
Indices of the abundance and biomass of adult flatfishes (mainly plaice and sole) are calculated by means of stratified tows in the southern and central North Sea. The results are incorporated in the survey database DATRAS, the databases of trawl surveys of ICES (www.datras.ices.dk). Currently, all Belgian survey data are stored at ILVO. The most recent data is stored in the national database of Smartfish. The data is expected to be uploaded to DATRAS on a yearly basis. The Belgian BTS data (2004-2019) and DYFS data (2011-2019) are already available in DATRAS. The historical DYFS- data (prior to 2011) and BTS data (1992-2003) are being prepared for uploading to DATRAS. Latest reports can be found on the website of WGBEAM (https://www.ices.dk/community/groups/Pages/WGBEAM.aspx), and in the case of the BTS on the RV BELGICA website ( https://odnature.naturalsciences.be/belgica/nl/campaign/1712) or for the DYFS on the MIDAS website (http://www.vliz.be/vmdcdata/midas/cruise.php?selectedcamp=103&showcamp=1).
Indices of the abundance and biomass of adult flatfishes (mainly plaice and sole) are calculated by means of stratified tows in the southern and central North Sea. The results are incorporated in the survey database DATRAS, the databases of trawl surveys of ICES (www.datras.ices.dk). Currently, all Belgian survey data are stored at ILVO. The most recent data is stored in the national database of Smartfish. The data is expected to be uploaded to DATRAS on a yearly basis. The Belgian BTS data (2004-2019) and DYFS data (2011-2019) are already available in DATRAS. The historical DYFS- data (prior to 2011) and BTS data (1992-2003) are being prepared for uploading to DATRAS. Latest reports can be found on the website of WGBEAM (https://www.ices.dk/community/groups/Pages/WGBEAM.aspx), and in the case of the BTS on the RV BELGICA website ( https://odnature.naturalsciences.be/belgica/nl/campaign/1712) or for the DYFS on the MIDAS website (http://www.vliz.be/vmdcdata/midas/cruise.php?selectedcamp=103&showcamp=1).
Data access
Related indicator/name
Contact
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
References