Member State report / Art11 / 2014-2020 / D6 / 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 D6 Sea-floor integrity/D1 Benthic habitats
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_D1_4_6_SeabedHabitats
Monitoring programme Reference existing programme
Monitoring programme Marine Unit ID
Q4e - Programme ID
ANSBE-D1, 4, 6 Seabed habitats
Q4f - Programme description
The Belgian MSFD monitoring programme ‘Biodiversity - seabed habitats’ aims at assessing the following ETs: • ET7 : The spatial extent and distribution of the EUNIS level 3 habitats (sandy mud to mud, muddy sands to sands and coarse grained sediments), as well as that of gravel beds fluctuate - relative to the reference state as described in Initial Assessment - within a margin limited to the accuracy of the current distribution maps • ET10: The Ecological Quality Ratio as determined by BEQI, indicative for benthic ecosystem structure and quality, has a minimum value of 0,60 in each of the habitat types • ET11: Positive trend in median adult density (or frequency of occurrence) of at least one species within the long-lived and/or slowly reproducing and key engineering benthic species groups in both mud to muddy sands and pure fine to coarse sands • ET12: Spring median benthic bioturbation potential (BPc) in the Abra alba habitat type is higher than 100 • ET13: Positive trend in median colony/body size of the sessile, long-lived and/or larger benthic species Buccinum undatum, Mytilus edulis, Flustra foliacea, Haliclona oculata and Alcyonium digitatum • ET14 – Positive trend in frequency of occurrence and median adult density of at least half of the key and long-lived species Ostrea edulis, Sabellaria spinulosa, Mytilus edulis, Buccinum undatum, Haliclona oculata, Alcyonium digitatum and Alcyonidium spp • ET15 – No loss or positive trend in species richness within all key hard substrate taxa, i.e. Porifera, Cnidaria, Bryozoa, Polychaeta, Malacostraca, Maxillopoda, Gastropoda, Bivalvia, Echinodermata and Ascidiacea • ET16 – Decreasing relative frequency of occurrence of damaged Asterias rubens (2+ cm arm length) and tube clusters of Pomatoceros triqueter, indicative for physical disturbance of the bottom (= pressure indicator), as to enhance natural development of the gravel bed ecosystem (= desired state) • ET17: For each of the scavenging seabirds species, are the mean densities over 5 consecutive years not below the minimum defined by the Birds Directive favourable conservation status Six sub-programmes can be discerned: • ANSBE-D1, 4, 6 Seabed-SP5 (delivering data to assess ET7), targeting a full-coverage seabed and transect seabed mapping of selected areas at EUNIS level 3; • ANSBE-D1, 4, 6 Seabed-SP6 (delivering data to assess ET10), targeting the quantification of a composite index based on density, biomass, species richness and species composition of the macrobenthos at selected stations in the BPNS; • ANSBE-D1, 4, 6 Seabed-SP7 (delivering data to assess ET11), targeting the quantification of long-lived and key engineering benthic species density at selected stations in the BPNS; • ANSBE-D1, 4, 6 Seabed-SP8 (delivering data to assess ET12), targeting the quantification of the macrobenthic community bioturbation potential at selected stations in the BPNS; • ANSBE-D1, 4, 6 Seabed-SP9 (delivering data to assess ET13 to 16), targeting body/colony size of characteristic hard substrate species, frequency of occurrence and densities in a non-bottom fisheries-impacted, a low impacted and regular fisheries-impacted area; • ANSBE-D1, 4, 6 Seabed-SP10 (delivering data to assess ET17), targeting multibeam bathymetry and backscatter measurements in combination with visual observations and seabed sampling in a gravel bed in the Hinder Banks region and a gravel bed in the Flemish Banks region
Q5e - Natural variability
  • Quantiative
Q5d - Adequacy for assessment of GES Q5d - Adequate data
N
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
By2018
Q5h - Plans to implement monitoring for GES assessment
A research proposal has been submitted to the Belgian Science Policy Office to strengthen capacity to develop improved methods and strategies for the acoustic mapping of seabed/habitat types in a monitoring context, hence emphasising on quantifying uncertainties in the mapping process needed for accurate change detection
Q6a -Relevant targets Q6a - Environmental target
Target 7 Target 10 Target 11 Target 12 Target 13 Target 14 Target 15 Target 16 Target 17
Q6a -Relevant targets Q6a - Associated indicator
Target 7 Target 10 Target 11 Target 12 Target 13 Target 14 Target 15 Target 16 Target 17
Q6b - Adequacy for assessment of targets Q6b_SuitableData
Y
Q6b - Adequacy for assessment of targets Q6b_EstablishedMethods
N
Q6b - Adequacy for assessment of targets Q6d_AdequateCapacity
N
Q6c - Target updating
N
Q6d - Description of programme for targets assessment
N.A.
Q6e - Gap-filling date for targets assessment
By2018
Q6f - Plans to implement monitoring for targets assessment
A research proposal has been submitted to the Belgian Science Policy Office to strengthen capacity to develop improved methods and strategies for the acoustic mapping of seabed/habitat types in a monitoring context, hence emphasising on quantifying uncertainties in the mapping process needed for accurate change detection
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
  • WFD
Reference sub-programme Sub-programme ID
Reference sub-programme Sub-programme name
Seabed habitats - distribution and extent
Q4g - Sub-programmes Sub-programme ID
Q4g - Sub-programmes Sub-programme name
Seabed habitats - distribution and extent
Q4k - Monitoring purpose
Q4l - Links of monitoring programmes of other Directives and Conventions
Q5c - Features Q5c - Habitats
Q5c - Features Q5c - Species list
Q5c - Features Q5c - Physical/Chemical features
  • TopographyBathymetry
Q5c - Features Q5c - Pressures
Q9a - Elements
Q5a - GES criteria Relevant GES criteria
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 6.1
  • 6.2
Q5b - GES indicators Relevant GES indicators
  • 1.2.1
  • 1.3.1
  • 1.4.1
  • 1.4.2
  • 1.5.1
  • 1.6.1
  • 1.6.3
  • 6.1.2
  • 6.2.2
  • 6.2.3
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
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
Monitoring strategy description
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Assessment of seafloor integrity is based on several monitoring programmes: (1) geographic analysis of data on all human activities affecting benthic habitats; (2) acoustic teledetection and ground truthing of changes in the extent and distribution of broad-scale habitats, with particular emphasis on gravel beds; (3) soft-sediment benthic sampling in the near-field of human activities; and (4) sampling and videography of strategically-selected natural hard-substrate benthos, based on the remote sensing. Yearly monitoring is foreseen, except for (2) which is done six yearly. The assessment aims to evaluate the status of the benthic biota with respect to the predominant pressures: e.g. sand extraction, disposal of dredged material, offshore wind farms and commercial fishing activities by bottom trawling. Trends in presence/absence of selected (morpho)species, richness, count, abundance and sediment parameters, as derived from the in-situ samples, provide the basis to monitor progress towards the targets specified within D6 Sea-floor integrity/D1 Biodiversity - Benthic Habitats.
Coverage of GES criteria
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Gaps and plans
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Individual monitoring programmes will be further fine-tuned and integrated. Methodological progress is on-going in the acoustic monitoring of changes in substrate type and its relation with benthos status. Overall, linking changes in natural versus anthropogenic-induced stresses as well as quantification of far-field effects and cumulative impacts requires further research. These developments are being followed up.
Related targets
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
  • D6.T1
  • D6.T10
  • D6.T2
  • D6.T3
  • D6.T4
  • D6.T5
  • D6.T6
  • D6.T7
  • D6.T8
  • D6.T9
Coverage of targets
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Related measures
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 2 - 'Definition targets to maintain MPAs. Development of the policy and management plans for the MPAs and their associated measures'
  • 25A - 'Ban on extraction of rock and gravel'
  • 25B - 'Test for the restoration of gravel beds'
  • 26C - 'Monitoring of the seabed protection areas'
  • 4A - 'Zoning: Delimitation of areas for extraction of sand'
  • 4B - 'Periodic closing of the extraction areas'
  • 4C - 'Authorisation conditions: maximum volume of extraction attributed'
  • 4D - 'Authorisation conditions: annual compensation/ allowance for follow-up activities (according to the material and the volume extracted)'
  • 4E - 'Follow-up and control of extraction activities'
  • 5A - 'Zoning: Delimitation of areas for the dumping of dredged materials'
  • 6C - 'Revision of extraction volumes (sand extraction)'
  • 6E - 'Limitation of fishing that impairs the seabed in the 'Vlaamse Banken' area (commercial and recreational fisheries); Follow-up of the seabed protection areas (used in the follow-up programme of the MSFD)'
  • 7C - 'Ban of certain activities in the special protection areas: civil construction, industrial activities, and commercial and advertising company activities'
  • 9 - 'Introduction of the SumWing technique, the diabolos (targeting and developing more selective techniques which have less impact on the seabed and which help to save energy), and raising awareness; supported by the Belgian operational programme and the national operational programme on fishing'
Coverage of measures
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Related monitoring programmes
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
  • ANSBE-P5-Seabed-physical
  • ANSBE-P6-Benthos-1-soft-sediment
  • ANSBE-P7-Benthos-2-epi-fish
  • ANSBE-P8-Benthos-3-windfarm
  • ANSBE-P9-Benthos-4-hard-substrate
Programme code
ANSBE-P5-Seabed-physical
ANSBE-P5-Seabed-physical
ANSBE-P5-Seabed-physical
ANSBE-P5-Seabed-physical
ANSBE-P6-Benthos-1-soft-sediment
ANSBE-P6-Benthos-1-soft-sediment
ANSBE-P6-Benthos-1-soft-sediment
ANSBE-P7-Benthos-2-epi-fish
ANSBE-P7-Benthos-2-epi-fish
ANSBE-P7-Benthos-2-epi-fish
ANSBE-P7-Benthos-2-epi-fish
ANSBE-P8-Benthos-3-windfarm
ANSBE-P8-Benthos-3-windfarm
ANSBE-P8-Benthos-3-windfarm
ANSBE-P9-Benthos-4-hard-substrate
ANSBE-P9-Benthos-4-hard-substrate
Programme name
Seafloor Integrity - Pressures, Physical loss and disturbance of seabed habitats
Seafloor Integrity - Pressures, Physical loss and disturbance of seabed habitats
Seafloor Integrity - Pressures, Physical loss and disturbance of seabed habitats
Seafloor Integrity - Pressures, Physical loss and disturbance of seabed habitats
Benthic soft-sediment environmental impact monitoring programme
Benthic soft-sediment environmental impact monitoring programme
Benthic soft-sediment environmental impact monitoring programme
Epibenthos and demersal fish environmental impact monitoring programme
Epibenthos and demersal fish environmental impact monitoring programme
Epibenthos and demersal fish environmental impact monitoring programme
Epibenthos and demersal fish environmental impact monitoring programme
Macrobenthos monitoring windfarm
Macrobenthos monitoring windfarm
Macrobenthos monitoring windfarm
Hard substrate benthos - community characteristics
Hard substrate benthos - community characteristics
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
New programme
New programme
New programme
Modified from 2014
Modified from 2014
Old programme codes
  • ANSBE-D1-4-6-Seabed-SP10
  • ANSBE-D1-4-6-Seabed-SP5
  • ANSBE-D1-4-6-Seabed-SP10
  • ANSBE-D1-4-6-Seabed-SP5
  • ANSBE-D1-4-6-Seabed-SP10
  • ANSBE-D1-4-6-Seabed-SP5
  • ANSBE-D1-4-6-Seabed-SP10
  • ANSBE-D1-4-6-Seabed-SP5
  • ANSBE-D1-4-6-Seabed-SP6
  • ANSBE-D1-4-6-Seabed-SP7
  • ANSBE-D1-4-6-Seabed-SP8
  • ANSBE-D2-NIS-SP12
  • ANSBE-D1-4-6-Seabed-SP6
  • ANSBE-D1-4-6-Seabed-SP7
  • ANSBE-D1-4-6-Seabed-SP8
  • ANSBE-D2-NIS-SP12
  • ANSBE-D1-4-6-Seabed-SP6
  • ANSBE-D1-4-6-Seabed-SP7
  • ANSBE-D1-4-6-Seabed-SP8
  • ANSBE-D2-NIS-SP12
  • ANSBE-D1-4-6-SP7
  • ANSBE-D2-NIS-SP12
  • ANSBE-D8-Contaminants-SP22
  • ANSBE-D1-4-6-SP7
  • ANSBE-D2-NIS-SP12
  • ANSBE-D8-Contaminants-SP22
  • ANSBE-D1-4-6-SP7
  • ANSBE-D2-NIS-SP12
  • ANSBE-D8-Contaminants-SP22
  • ANSBE-D1-4-6-SP7
  • ANSBE-D2-NIS-SP12
  • ANSBE-D8-Contaminants-SP22
  • ANSBE-D1-4-6-Seabed-SP9
  • ANSBE-D1-4-6-Seabed-SP9
Programme description
Physical changes of the seabed environment are assessed based on: a. Geographic analysis of all human activities contributing to physical loss and disturbance of seabed habitats. b. Acoustic remote sensing and ground truthing to evaluate changes in the spatial extent and distribution of the EUNIS level 2 habitats (mud, sand, and coarse-grained sediments), as well as gravel beds. Monitoring should allow assessing whether the spatial extent of these habitats fluctuates - relative to the reference state as described in Initial Assessment - within a margin limited to the accuracy of the current distribution maps. c. Acoustic remote sensing and ground truthing to evaluate the ratio of the hard substrate surface area (i.e. surfaces that are colonized by hard substrate epifauna) over soft sediment surface area (i.e. surfaces overtopping hard substrates and preventing hard substrate fauna development). This should not show a negative trend. International cooperation is on-going in the technical group TG Seabed (EU DG ENV). This programme contributes to environmental targets D6.1, D6.2 and D6.3. (Former programme ANSBE-D1-4-6-Seabed-SP5)
Physical changes of the seabed environment are assessed based on: a. Geographic analysis of all human activities contributing to physical loss and disturbance of seabed habitats. b. Acoustic remote sensing and ground truthing to evaluate changes in the spatial extent and distribution of the EUNIS level 2 habitats (mud, sand, and coarse-grained sediments), as well as gravel beds. Monitoring should allow assessing whether the spatial extent of these habitats fluctuates - relative to the reference state as described in Initial Assessment - within a margin limited to the accuracy of the current distribution maps. c. Acoustic remote sensing and ground truthing to evaluate the ratio of the hard substrate surface area (i.e. surfaces that are colonized by hard substrate epifauna) over soft sediment surface area (i.e. surfaces overtopping hard substrates and preventing hard substrate fauna development). This should not show a negative trend. International cooperation is on-going in the technical group TG Seabed (EU DG ENV). This programme contributes to environmental targets D6.1, D6.2 and D6.3. (Former programme ANSBE-D1-4-6-Seabed-SP5)
Physical changes of the seabed environment are assessed based on: a. Geographic analysis of all human activities contributing to physical loss and disturbance of seabed habitats. b. Acoustic remote sensing and ground truthing to evaluate changes in the spatial extent and distribution of the EUNIS level 2 habitats (mud, sand, and coarse-grained sediments), as well as gravel beds. Monitoring should allow assessing whether the spatial extent of these habitats fluctuates - relative to the reference state as described in Initial Assessment - within a margin limited to the accuracy of the current distribution maps. c. Acoustic remote sensing and ground truthing to evaluate the ratio of the hard substrate surface area (i.e. surfaces that are colonized by hard substrate epifauna) over soft sediment surface area (i.e. surfaces overtopping hard substrates and preventing hard substrate fauna development). This should not show a negative trend. International cooperation is on-going in the technical group TG Seabed (EU DG ENV). This programme contributes to environmental targets D6.1, D6.2 and D6.3. (Former programme ANSBE-D1-4-6-Seabed-SP5)
Physical changes of the seabed environment are assessed based on: a. Geographic analysis of all human activities contributing to physical loss and disturbance of seabed habitats. b. Acoustic remote sensing and ground truthing to evaluate changes in the spatial extent and distribution of the EUNIS level 2 habitats (mud, sand, and coarse-grained sediments), as well as gravel beds. Monitoring should allow assessing whether the spatial extent of these habitats fluctuates - relative to the reference state as described in Initial Assessment - within a margin limited to the accuracy of the current distribution maps. c. Acoustic remote sensing and ground truthing to evaluate the ratio of the hard substrate surface area (i.e. surfaces that are colonized by hard substrate epifauna) over soft sediment surface area (i.e. surfaces overtopping hard substrates and preventing hard substrate fauna development). This should not show a negative trend. International cooperation is on-going in the technical group TG Seabed (EU DG ENV). This programme contributes to environmental targets D6.1, D6.2 and D6.3. (Former programme ANSBE-D1-4-6-Seabed-SP5)
This programme covers the soft-sediment benthic monitoring by ILVO, in the framework of the environmental impact assessment of the dredge disposal sites and sand extraction areas in the Belgian part of the North Sea. More info at https://www.ilvo.vlaanderen.be/Aquaticenvironmentandquality/tabid/6502/language/en-US/Default.aspx#.Xh2wn8hKhaQ. This is a classical benthic monitoring, but in the meantime we are investigating certain innovative monitoring methods (genetic, imagery). This innovation in monitoring will not replace the current one before 2024. This programme is overarching the specific monitoring programmes outlined in 2014 (codes ANSBE-D1-4-6-SP6, SP7 and SP8) and covers the environmental targets BEQI (D6.4), long-living species D6.5), BPc (D6.6) and alien species (D2.1).
This programme covers the soft-sediment benthic monitoring by ILVO, in the framework of the environmental impact assessment of the dredge disposal sites and sand extraction areas in the Belgian part of the North Sea. More info at https://www.ilvo.vlaanderen.be/Aquaticenvironmentandquality/tabid/6502/language/en-US/Default.aspx#.Xh2wn8hKhaQ. This is a classical benthic monitoring, but in the meantime we are investigating certain innovative monitoring methods (genetic, imagery). This innovation in monitoring will not replace the current one before 2024. This programme is overarching the specific monitoring programmes outlined in 2014 (codes ANSBE-D1-4-6-SP6, SP7 and SP8) and covers the environmental targets BEQI (D6.4), long-living species D6.5), BPc (D6.6) and alien species (D2.1).
This programme covers the soft-sediment benthic monitoring by ILVO, in the framework of the environmental impact assessment of the dredge disposal sites and sand extraction areas in the Belgian part of the North Sea. More info at https://www.ilvo.vlaanderen.be/Aquaticenvironmentandquality/tabid/6502/language/en-US/Default.aspx#.Xh2wn8hKhaQ. This is a classical benthic monitoring, but in the meantime we are investigating certain innovative monitoring methods (genetic, imagery). This innovation in monitoring will not replace the current one before 2024. This programme is overarching the specific monitoring programmes outlined in 2014 (codes ANSBE-D1-4-6-SP6, SP7 and SP8) and covers the environmental targets BEQI (D6.4), long-living species D6.5), BPc (D6.6) and alien species (D2.1).
This programme covers the monitoring of soft-sediment epibenthos and demersal fish by ILVO, in the frame of the environmental impact assessment of the dredge disposal sites and sand extraction areas in the Belgian part of the North Sea. More info at https://www.ilvo.vlaanderen.be/Aquaticenvironmentandquality/tabid/6502/language/en-US/Default.aspx#.Xh2wn8hKhaQ. This programme covers the environmental targets for long-lived species (D6.6), non-indigenous species (D2.1) and fish diseases (D8.5).
This programme covers the monitoring of soft-sediment epibenthos and demersal fish by ILVO, in the frame of the environmental impact assessment of the dredge disposal sites and sand extraction areas in the Belgian part of the North Sea. More info at https://www.ilvo.vlaanderen.be/Aquaticenvironmentandquality/tabid/6502/language/en-US/Default.aspx#.Xh2wn8hKhaQ. This programme covers the environmental targets for long-lived species (D6.6), non-indigenous species (D2.1) and fish diseases (D8.5).
This programme covers the monitoring of soft-sediment epibenthos and demersal fish by ILVO, in the frame of the environmental impact assessment of the dredge disposal sites and sand extraction areas in the Belgian part of the North Sea. More info at https://www.ilvo.vlaanderen.be/Aquaticenvironmentandquality/tabid/6502/language/en-US/Default.aspx#.Xh2wn8hKhaQ. This programme covers the environmental targets for long-lived species (D6.6), non-indigenous species (D2.1) and fish diseases (D8.5).
This programme covers the monitoring of soft-sediment epibenthos and demersal fish by ILVO, in the frame of the environmental impact assessment of the dredge disposal sites and sand extraction areas in the Belgian part of the North Sea. More info at https://www.ilvo.vlaanderen.be/Aquaticenvironmentandquality/tabid/6502/language/en-US/Default.aspx#.Xh2wn8hKhaQ. This programme covers the environmental targets for long-lived species (D6.6), non-indigenous species (D2.1) and fish diseases (D8.5).
Offshore Windfarm macrobenthos and sediment monitoring programme of the Marine Biology Research Group at Ghent University. This programme contributes to the environmental targets D6.4, D6.5 and D2.1.
Offshore Windfarm macrobenthos and sediment monitoring programme of the Marine Biology Research Group at Ghent University. This programme contributes to the environmental targets D6.4, D6.5 and D2.1.
Offshore Windfarm macrobenthos and sediment monitoring programme of the Marine Biology Research Group at Ghent University. This programme contributes to the environmental targets D6.4, D6.5 and D2.1.
Periodic collection of environmental spatial data (by means of remote sensing) and sedimentological and biological data based on site verification (by direct physical sampling) at selected locations, deemed representative of broader areas. This programme contributes to environmental objectives D6.7, D6.8, D6.9 and D6.10.
Periodic collection of environmental spatial data (by means of remote sensing) and sedimentological and biological data based on site verification (by direct physical sampling) at selected locations, deemed representative of broader areas. This programme contributes to environmental objectives D6.7, D6.8, D6.9 and D6.10.
Monitoring purpose
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • 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
  • 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
Other policies and conventions
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Habitats Directive
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
Regional cooperation - coordinating body
Regional cooperation - countries involved
Regional cooperation - implementation level
Monitoring details
1) Monitoring approach: a. Spatio-temporal analysis of human activity data (presence/absence), as obtained from the competent authorities, in a geographic information system (from 2011). b. Risk-based monitoring approach combining multibeam bathymetry/backscatter and ground truthing, targeting detecting changes in the distribution and extent of broad-scale habitat types. Surveys are conducted along pre-defined transects and boxes (from 2015). c. Full-coverage multibeam bathymetry/backscatter and ground truthing in two selected gravel zones (from 2014). 2) Proportion of geographic scope covered by sampling: a. Belgian part of the North Sea (BPNS) b. Belgian part of the North Sea, focusing on the extent and distribution of the benthic broad-scale habitat types c. Two test zones in the gravel beds 3) Frequency of sampling: a. Yearly follow-up of human activities b. Six yearly c. Yearly More information about the treatment and analyses can be found in: https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_assessments_2018_nl.pdf en https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_annex_fysisch_verlies_en.pdf
1) Monitoring approach: a. Spatio-temporal analysis of human activity data (presence/absence), as obtained from the competent authorities, in a geographic information system (from 2011). b. Risk-based monitoring approach combining multibeam bathymetry/backscatter and ground truthing, targeting detecting changes in the distribution and extent of broad-scale habitat types. Surveys are conducted along pre-defined transects and boxes (from 2015). c. Full-coverage multibeam bathymetry/backscatter and ground truthing in two selected gravel zones (from 2014). 2) Proportion of geographic scope covered by sampling: a. Belgian part of the North Sea (BPNS) b. Belgian part of the North Sea, focusing on the extent and distribution of the benthic broad-scale habitat types c. Two test zones in the gravel beds 3) Frequency of sampling: a. Yearly follow-up of human activities b. Six yearly c. Yearly More information about the treatment and analyses can be found in: https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_assessments_2018_nl.pdf en https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_annex_fysisch_verlies_en.pdf
1) Monitoring approach: a. Spatio-temporal analysis of human activity data (presence/absence), as obtained from the competent authorities, in a geographic information system (from 2011). b. Risk-based monitoring approach combining multibeam bathymetry/backscatter and ground truthing, targeting detecting changes in the distribution and extent of broad-scale habitat types. Surveys are conducted along pre-defined transects and boxes (from 2015). c. Full-coverage multibeam bathymetry/backscatter and ground truthing in two selected gravel zones (from 2014). 2) Proportion of geographic scope covered by sampling: a. Belgian part of the North Sea (BPNS) b. Belgian part of the North Sea, focusing on the extent and distribution of the benthic broad-scale habitat types c. Two test zones in the gravel beds 3) Frequency of sampling: a. Yearly follow-up of human activities b. Six yearly c. Yearly More information about the treatment and analyses can be found in: https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_assessments_2018_nl.pdf en https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_annex_fysisch_verlies_en.pdf
1) Monitoring approach: a. Spatio-temporal analysis of human activity data (presence/absence), as obtained from the competent authorities, in a geographic information system (from 2011). b. Risk-based monitoring approach combining multibeam bathymetry/backscatter and ground truthing, targeting detecting changes in the distribution and extent of broad-scale habitat types. Surveys are conducted along pre-defined transects and boxes (from 2015). c. Full-coverage multibeam bathymetry/backscatter and ground truthing in two selected gravel zones (from 2014). 2) Proportion of geographic scope covered by sampling: a. Belgian part of the North Sea (BPNS) b. Belgian part of the North Sea, focusing on the extent and distribution of the benthic broad-scale habitat types c. Two test zones in the gravel beds 3) Frequency of sampling: a. Yearly follow-up of human activities b. Six yearly c. Yearly More information about the treatment and analyses can be found in: https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_assessments_2018_nl.pdf en https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_annex_fysisch_verlies_en.pdf
Benthos (animals retrieved on a 1mm sieve) is collected by a Van Veen grab at different locations and habitats within the Belgian part of the North Sea. The spatial and temporal distribution of those samples depends on the occurrence and intensity of human activities in different areas. The exact number of samples per year and area depends on which sand extraction and disposal area is visited (certain rotation system (3-yearly) + depending on where the activity is going on). Samples are also taken at control stations, locations outside the direct impact sphere of the activity. Besides, a few long-term monitoring locations are regularly sampled. Details of sampling records in the past and what is expected the coming years is given in annex. Monitoring is ongoing since 1979, but with a more standardized, comparable design from 2006 onwards. International cooperation is currently limited to knowledge exchange within OSPAR COBAM, benthic expert group.
Benthos (animals retrieved on a 1mm sieve) is collected by a Van Veen grab at different locations and habitats within the Belgian part of the North Sea. The spatial and temporal distribution of those samples depends on the occurrence and intensity of human activities in different areas. The exact number of samples per year and area depends on which sand extraction and disposal area is visited (certain rotation system (3-yearly) + depending on where the activity is going on). Samples are also taken at control stations, locations outside the direct impact sphere of the activity. Besides, a few long-term monitoring locations are regularly sampled. Details of sampling records in the past and what is expected the coming years is given in annex. Monitoring is ongoing since 1979, but with a more standardized, comparable design from 2006 onwards. International cooperation is currently limited to knowledge exchange within OSPAR COBAM, benthic expert group.
Benthos (animals retrieved on a 1mm sieve) is collected by a Van Veen grab at different locations and habitats within the Belgian part of the North Sea. The spatial and temporal distribution of those samples depends on the occurrence and intensity of human activities in different areas. The exact number of samples per year and area depends on which sand extraction and disposal area is visited (certain rotation system (3-yearly) + depending on where the activity is going on). Samples are also taken at control stations, locations outside the direct impact sphere of the activity. Besides, a few long-term monitoring locations are regularly sampled. Details of sampling records in the past and what is expected the coming years is given in annex. Monitoring is ongoing since 1979, but with a more standardized, comparable design from 2006 onwards. International cooperation is currently limited to knowledge exchange within OSPAR COBAM, benthic expert group.
The epibenthos and demersal fish are collected by 8m beam trawl with 22mm mesh at different locations and habitats within the Belgian part of the North Sea. The spatial and temporal distribution of those samples depends on the occurrence and intensity of human activities in different areas. The exact number of samples per year and area depends on which sand extraction and disposal area is visited (certain rotation system + depending on where the activity is going on). The windfarm area is sampled every year, but with variation in the specific concession areas sampled. In addition, a number of long-term monitoring stations are sampled on a regular basis. The epibenthos and demersal fish are determined to species level, counted and weighted (not fish) or length measured (fish). The dab (Limanda limanda) in the tracks (up to a maximum of 500 individuals for respectively the coastal and offshore assessment area) are investigated for external fish diseases, following the ICES TIMES guidelines. This programme is covering the environmental targets long-living species (D6.6), alien species (D2.1) and fish diseases (D8.5). From 2006 onwards, monitoring is executed following a more standardized, comparable design.
The epibenthos and demersal fish are collected by 8m beam trawl with 22mm mesh at different locations and habitats within the Belgian part of the North Sea. The spatial and temporal distribution of those samples depends on the occurrence and intensity of human activities in different areas. The exact number of samples per year and area depends on which sand extraction and disposal area is visited (certain rotation system + depending on where the activity is going on). The windfarm area is sampled every year, but with variation in the specific concession areas sampled. In addition, a number of long-term monitoring stations are sampled on a regular basis. The epibenthos and demersal fish are determined to species level, counted and weighted (not fish) or length measured (fish). The dab (Limanda limanda) in the tracks (up to a maximum of 500 individuals for respectively the coastal and offshore assessment area) are investigated for external fish diseases, following the ICES TIMES guidelines. This programme is covering the environmental targets long-living species (D6.6), alien species (D2.1) and fish diseases (D8.5). From 2006 onwards, monitoring is executed following a more standardized, comparable design.
The epibenthos and demersal fish are collected by 8m beam trawl with 22mm mesh at different locations and habitats within the Belgian part of the North Sea. The spatial and temporal distribution of those samples depends on the occurrence and intensity of human activities in different areas. The exact number of samples per year and area depends on which sand extraction and disposal area is visited (certain rotation system + depending on where the activity is going on). The windfarm area is sampled every year, but with variation in the specific concession areas sampled. In addition, a number of long-term monitoring stations are sampled on a regular basis. The epibenthos and demersal fish are determined to species level, counted and weighted (not fish) or length measured (fish). The dab (Limanda limanda) in the tracks (up to a maximum of 500 individuals for respectively the coastal and offshore assessment area) are investigated for external fish diseases, following the ICES TIMES guidelines. This programme is covering the environmental targets long-living species (D6.6), alien species (D2.1) and fish diseases (D8.5). From 2006 onwards, monitoring is executed following a more standardized, comparable design.
The epibenthos and demersal fish are collected by 8m beam trawl with 22mm mesh at different locations and habitats within the Belgian part of the North Sea. The spatial and temporal distribution of those samples depends on the occurrence and intensity of human activities in different areas. The exact number of samples per year and area depends on which sand extraction and disposal area is visited (certain rotation system + depending on where the activity is going on). The windfarm area is sampled every year, but with variation in the specific concession areas sampled. In addition, a number of long-term monitoring stations are sampled on a regular basis. The epibenthos and demersal fish are determined to species level, counted and weighted (not fish) or length measured (fish). The dab (Limanda limanda) in the tracks (up to a maximum of 500 individuals for respectively the coastal and offshore assessment area) are investigated for external fish diseases, following the ICES TIMES guidelines. This programme is covering the environmental targets long-living species (D6.6), alien species (D2.1) and fish diseases (D8.5). From 2006 onwards, monitoring is executed following a more standardized, comparable design.
The macrobenthos (animals retrieved on a 1mm sieve) are collected by a Van Veen grab at different locations and habitats within the OWFs C-Power and Belwind at the Belgian Part of the North Sea. These samples are compared to reference areas close to the studied OWFs. From each Van Veen grab, a sediment sample is retrieved for benthic habitat characterization (granulometric measurements: median grain size (µm) and fine sediment fraction (% within 125-250 µm); total organic matter content (%)). Frequency: from T0 (before construction) onwards, yearly except when windfarm in construction phase. Since 2005 onwards in C-Power (Thornton bank and Goote Bank); since 2008 onwards in Belwind (Bligh Bank), mainly in autumn, with different sampling schemes.
The macrobenthos (animals retrieved on a 1mm sieve) are collected by a Van Veen grab at different locations and habitats within the OWFs C-Power and Belwind at the Belgian Part of the North Sea. These samples are compared to reference areas close to the studied OWFs. From each Van Veen grab, a sediment sample is retrieved for benthic habitat characterization (granulometric measurements: median grain size (µm) and fine sediment fraction (% within 125-250 µm); total organic matter content (%)). Frequency: from T0 (before construction) onwards, yearly except when windfarm in construction phase. Since 2005 onwards in C-Power (Thornton bank and Goote Bank); since 2008 onwards in Belwind (Bligh Bank), mainly in autumn, with different sampling schemes.
The macrobenthos (animals retrieved on a 1mm sieve) are collected by a Van Veen grab at different locations and habitats within the OWFs C-Power and Belwind at the Belgian Part of the North Sea. These samples are compared to reference areas close to the studied OWFs. From each Van Veen grab, a sediment sample is retrieved for benthic habitat characterization (granulometric measurements: median grain size (µm) and fine sediment fraction (% within 125-250 µm); total organic matter content (%)). Frequency: from T0 (before construction) onwards, yearly except when windfarm in construction phase. Since 2005 onwards in C-Power (Thornton bank and Goote Bank); since 2008 onwards in Belwind (Bligh Bank), mainly in autumn, with different sampling schemes.
The monitoring consists of a periodic assessment of benthic communities at fixed locations. Four stations have been designated in the Northern Exploration Area (area overlapping with area designated for the exploration of the potential of marine aggregate extraction and for the protection of the seabed in Marine Spatial Plan 2020-2026). A transect station will be established in the Hinderbanken. Sampling is implemented by Hammon grab and underwater videography. In-situ samples are stored and processed at RBINS facilities (Oostende) according to in-house protocols of faunal analysis. Tabulation of species data (count, abundance and richness). Underwater videography: stored and processed at RBINS (Brussels) according to currently developing methodologies w.r.t. semi-automated image classification and feature extraction.
The monitoring consists of a periodic assessment of benthic communities at fixed locations. Four stations have been designated in the Northern Exploration Area (area overlapping with area designated for the exploration of the potential of marine aggregate extraction and for the protection of the seabed in Marine Spatial Plan 2020-2026). A transect station will be established in the Hinderbanken. Sampling is implemented by Hammon grab and underwater videography. In-situ samples are stored and processed at RBINS facilities (Oostende) according to in-house protocols of faunal analysis. Tabulation of species data (count, abundance and richness). Underwater videography: stored and processed at RBINS (Brussels) according to currently developing methodologies w.r.t. semi-automated image classification and feature extraction.
Features
Physical loss of the seabed
Physical disturbance to seabed
Benthic broad habitats
Benthic broad habitats
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Demersal shelf fish
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Physical loss of the seabed
Physical disturbance to seabed
Benthic broad habitats
Benthic broad habitats
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Demersal shelf fish
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Physical loss of the seabed
Physical disturbance to seabed
Benthic broad habitats
Benthic broad habitats
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Demersal shelf fish
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Physical loss of the seabed
Physical disturbance to seabed
Benthic broad habitats
Benthic broad habitats
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Demersal shelf fish
Newly introduced non-indigenous species
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Elements
  • Not Applicable
  • Not Applicable
  • Benthic habitats
  • Benthic habitats
  • Not Applicable
  • Benthic habitats
  • Benthic habitats
  • Not Applicable
  • Benthic habitats
  • Benthic habitats
  • Limanda limanda
  • Not Applicable
  • Infralittoral coarse sediment
  • Infralittoral sand
  • Offshore circalittoral coarse sediment
  • Offshore circalittoral coarse sediment
GES criteria
D6C1
D6C2
D6C3
D6C5
D2C1
D6C3
D6C5
D2C1
D6C3
D6C5
D8C2
D2C1
D6C3
D6C5
D6C3
D6C5
Parameters
  • Extent
  • Extent
  • Extent
  • Extent
  • Presence
  • Extent
  • Other
  • Extent
  • Other
  • Presence
  • Extent
  • Other
  • Extent
  • Other
  • Other
  • Presence
  • Extent
  • Other
  • Extent
  • Other
  • Other
  • Other
Parameter Other
species composition, biomass, abundance
species composition, biomass, abundance
species composition, abundance, biomass
species composition, abundance, biomass
Fish Disease Index
species composition, abundance, biomass
species composition, abundance, biomass
Abundance of species, size
Abundance of species, size
Spatial scope
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • EEZ (or similar)
  • Territorial waters
  • EEZ (or similar)
  • Territorial waters
  • EEZ (or similar)
  • Territorial waters
  • EEZ (or similar)
  • Territorial waters
  • EEZ (or similar)
  • Territorial waters
Marine reporting units
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
Temporal scope (start date - end date)
2011-9999
2011-9999
2011-9999
2011-9999
1979-9999
1979-9999
1979-9999
1985-9999
1985-9999
1985-9999
1985-9999
2005-9999
2005-9999
2005-9999
2015-9999
2015-9999
Monitoring frequency
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
2-yearly
2-yearly
Monitoring type
  • Other
  • Other
  • Other
  • Other
  • 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 offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • Remote surveillance
  • In-situ sampling offshore
  • Remote surveillance
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
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
Monitoring method other
a. Geographic analysis b. Acoustic remote sensing (multibeam depth and backscatter), as well as ground truthing (samples and visual observations) c. Idem as for (b) References • Kint, L., Montereale Gavazzi, G., Van Lancker, V., 2018. Kaderrichtlijn Mariene Strategie. Beschrijvend element 6: Zeebodemintegriteit. Ruimtelijke analyse fysisch verlies en fysische verstoring. Brussel, Koninklijk Belgisch Instituut voor Natuurwetenschappen, 40 p. URL: https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_annex_fysisch_verlies_en_verstoring_2018_nl.pdf • Montereale-Gavazzi, G., Roche, M., Lurton, X., Degrendele, K., Terseleer, N., & Van Lancker, V., 2018. Seafloor change detection using multibeam echosounder backscatter: case study on the Belgian part of the North Sea. Marine Geophysical Research, 39(1-2), 229-247. •Montereale Gavazzi, G. (2019). Development of seafloor mapping strategies supporting integrated marine management: application of seafloor backscatter by multibeam echosounders. PhD Thesis. Ghent University, Faculty of Sciences: Gent. xxiii, 366 pp. •Roche, M., Degrendele, K., Vrignaud, C., Loyer, S., Le Bas, T., Augustin, J. M., & Lurton, X., 2018. Control of the repeatability of high frequency multibeam echosounder backscatter by using natural reference areas. Marine Geophysical Research, 39(1-2), 89-104. •Van Lancker, V., Kint, L., Montereale-Gavazzi, G., 2018. Fysische verstoring en verlies van de zeebodem (D6). In: Belgische Staat. Art. 17 Beoordeling voor de Belgische mariene wateren – Richtlijn 2008/59/EG. Kaderrichtlijn Mariene Strategie. BMM, Federale Overheidsdienst Volksgezondheid, Veiligheid van de Voedselketen en Leefmilieu, Brussel, België. URL https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_assessments_2018_nl.pdf
a. Geographic analysis b. Acoustic remote sensing (multibeam depth and backscatter), as well as ground truthing (samples and visual observations) c. Idem as for (b) References • Kint, L., Montereale Gavazzi, G., Van Lancker, V., 2018. Kaderrichtlijn Mariene Strategie. Beschrijvend element 6: Zeebodemintegriteit. Ruimtelijke analyse fysisch verlies en fysische verstoring. Brussel, Koninklijk Belgisch Instituut voor Natuurwetenschappen, 40 p. URL: https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_annex_fysisch_verlies_en_verstoring_2018_nl.pdf • Montereale-Gavazzi, G., Roche, M., Lurton, X., Degrendele, K., Terseleer, N., & Van Lancker, V., 2018. Seafloor change detection using multibeam echosounder backscatter: case study on the Belgian part of the North Sea. Marine Geophysical Research, 39(1-2), 229-247. •Montereale Gavazzi, G. (2019). Development of seafloor mapping strategies supporting integrated marine management: application of seafloor backscatter by multibeam echosounders. PhD Thesis. Ghent University, Faculty of Sciences: Gent. xxiii, 366 pp. •Roche, M., Degrendele, K., Vrignaud, C., Loyer, S., Le Bas, T., Augustin, J. M., & Lurton, X., 2018. Control of the repeatability of high frequency multibeam echosounder backscatter by using natural reference areas. Marine Geophysical Research, 39(1-2), 89-104. •Van Lancker, V., Kint, L., Montereale-Gavazzi, G., 2018. Fysische verstoring en verlies van de zeebodem (D6). In: Belgische Staat. Art. 17 Beoordeling voor de Belgische mariene wateren – Richtlijn 2008/59/EG. Kaderrichtlijn Mariene Strategie. BMM, Federale Overheidsdienst Volksgezondheid, Veiligheid van de Voedselketen en Leefmilieu, Brussel, België. URL https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_assessments_2018_nl.pdf
a. Geographic analysis b. Acoustic remote sensing (multibeam depth and backscatter), as well as ground truthing (samples and visual observations) c. Idem as for (b) References • Kint, L., Montereale Gavazzi, G., Van Lancker, V., 2018. Kaderrichtlijn Mariene Strategie. Beschrijvend element 6: Zeebodemintegriteit. Ruimtelijke analyse fysisch verlies en fysische verstoring. Brussel, Koninklijk Belgisch Instituut voor Natuurwetenschappen, 40 p. URL: https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_annex_fysisch_verlies_en_verstoring_2018_nl.pdf • Montereale-Gavazzi, G., Roche, M., Lurton, X., Degrendele, K., Terseleer, N., & Van Lancker, V., 2018. Seafloor change detection using multibeam echosounder backscatter: case study on the Belgian part of the North Sea. Marine Geophysical Research, 39(1-2), 229-247. •Montereale Gavazzi, G. (2019). Development of seafloor mapping strategies supporting integrated marine management: application of seafloor backscatter by multibeam echosounders. PhD Thesis. Ghent University, Faculty of Sciences: Gent. xxiii, 366 pp. •Roche, M., Degrendele, K., Vrignaud, C., Loyer, S., Le Bas, T., Augustin, J. M., & Lurton, X., 2018. Control of the repeatability of high frequency multibeam echosounder backscatter by using natural reference areas. Marine Geophysical Research, 39(1-2), 89-104. •Van Lancker, V., Kint, L., Montereale-Gavazzi, G., 2018. Fysische verstoring en verlies van de zeebodem (D6). In: Belgische Staat. Art. 17 Beoordeling voor de Belgische mariene wateren – Richtlijn 2008/59/EG. Kaderrichtlijn Mariene Strategie. BMM, Federale Overheidsdienst Volksgezondheid, Veiligheid van de Voedselketen en Leefmilieu, Brussel, België. URL https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_assessments_2018_nl.pdf
a. Geographic analysis b. Acoustic remote sensing (multibeam depth and backscatter), as well as ground truthing (samples and visual observations) c. Idem as for (b) References • Kint, L., Montereale Gavazzi, G., Van Lancker, V., 2018. Kaderrichtlijn Mariene Strategie. Beschrijvend element 6: Zeebodemintegriteit. Ruimtelijke analyse fysisch verlies en fysische verstoring. Brussel, Koninklijk Belgisch Instituut voor Natuurwetenschappen, 40 p. URL: https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_annex_fysisch_verlies_en_verstoring_2018_nl.pdf • Montereale-Gavazzi, G., Roche, M., Lurton, X., Degrendele, K., Terseleer, N., & Van Lancker, V., 2018. Seafloor change detection using multibeam echosounder backscatter: case study on the Belgian part of the North Sea. Marine Geophysical Research, 39(1-2), 229-247. •Montereale Gavazzi, G. (2019). Development of seafloor mapping strategies supporting integrated marine management: application of seafloor backscatter by multibeam echosounders. PhD Thesis. Ghent University, Faculty of Sciences: Gent. xxiii, 366 pp. •Roche, M., Degrendele, K., Vrignaud, C., Loyer, S., Le Bas, T., Augustin, J. M., & Lurton, X., 2018. Control of the repeatability of high frequency multibeam echosounder backscatter by using natural reference areas. Marine Geophysical Research, 39(1-2), 89-104. •Van Lancker, V., Kint, L., Montereale-Gavazzi, G., 2018. Fysische verstoring en verlies van de zeebodem (D6). In: Belgische Staat. Art. 17 Beoordeling voor de Belgische mariene wateren – Richtlijn 2008/59/EG. Kaderrichtlijn Mariene Strategie. BMM, Federale Overheidsdienst Volksgezondheid, Veiligheid van de Voedselketen en Leefmilieu, Brussel, België. URL https://odnature.naturalsciences.be/downloads/msfd/assessments_2018/nl/d6_assessments_2018_nl.pdf
Sampling is done with a Van Veen grab (0.1m2) follows the ISO standard (ISO 16665:2014(E)) (Water quality - Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna) for the sampling, processing and analyses. The laboratory procedure for analysing macrobenthic samples is since 24/05/2011 accredited under the BELAC ISO17025 norm (ILVO-DIER-ANIMALAB; CertificaatNr: BELAC T-315).
Sampling is done with a Van Veen grab (0.1m2) follows the ISO standard (ISO 16665:2014(E)) (Water quality - Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna) for the sampling, processing and analyses. The laboratory procedure for analysing macrobenthic samples is since 24/05/2011 accredited under the BELAC ISO17025 norm (ILVO-DIER-ANIMALAB; CertificaatNr: BELAC T-315).
Sampling is done with a Van Veen grab (0.1m2) follows the ISO standard (ISO 16665:2014(E)) (Water quality - Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna) for the sampling, processing and analyses. The laboratory procedure for analysing macrobenthic samples is since 24/05/2011 accredited under the BELAC ISO17025 norm (ILVO-DIER-ANIMALAB; CertificaatNr: BELAC T-315).
Epibenthos and demersal fish is sampled by a 8m beam trawl - the protocol outlined in the ICES Guidelines for the study of the epibenthos of subtidal environments, No. 42, Febr 2009 is followed. Fish Diseases: http://info.ices.dk/pubs/times/times19/TIMES19.pdf
Epibenthos and demersal fish is sampled by a 8m beam trawl - the protocol outlined in the ICES Guidelines for the study of the epibenthos of subtidal environments, No. 42, Febr 2009 is followed. Fish Diseases: http://info.ices.dk/pubs/times/times19/TIMES19.pdf
Epibenthos and demersal fish is sampled by a 8m beam trawl - the protocol outlined in the ICES Guidelines for the study of the epibenthos of subtidal environments, No. 42, Febr 2009 is followed. Fish Diseases: http://info.ices.dk/pubs/times/times19/TIMES19.pdf
Epibenthos and demersal fish is sampled by a 8m beam trawl - the protocol outlined in the ICES Guidelines for the study of the epibenthos of subtidal environments, No. 42, Febr 2009 is followed. Fish Diseases: http://info.ices.dk/pubs/times/times19/TIMES19.pdf
Sampling is done with a Van Veen grab (0.1m²) following the ISO standard (ISO 16665:2014(E)) (Water quality - Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna) for the sampling, processing and analyses.
Sampling is done with a Van Veen grab (0.1m²) following the ISO standard (ISO 16665:2014(E)) (Water quality - Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna) for the sampling, processing and analyses.
Sampling is done with a Van Veen grab (0.1m²) following the ISO standard (ISO 16665:2014(E)) (Water quality - Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna) for the sampling, processing and analyses.
Community analysis from Hammon grab samples. Semi-automated image-analysis from underwater still frames and videos for the detection of bio-encrusting and flourishing epibenthos. Characterization of morpho-species.
Community analysis from Hammon grab samples. Semi-automated image-analysis from underwater still frames and videos for the detection of bio-encrusting and flourishing epibenthos. Characterization of morpho-species.
Quality control
a. Detailed metadata are provided per human activity, as well as a quality factor. b. and c. Depth recordings using multibeam technology are linked to precision positioning, making them accurate in place and space. RV Belgicas EM3002D multibeam echo sounder complies with the IHO S44 Special Order quality criteria. Under this IHO standard, the total vertical uncertainty of the depth measurements ± 0.26 m and ± 0.34 m in 10 m and 30 m water depths, respectively (within a confidence interval of ± 95%). There are yet no quality criteria for multibeam backscatter values, which means that data sets of different ships and/or different campaigns cannot be brought together in the original format. Therefore, a seabed classification is performed per dataset and afterwards the classifications are combined into one thematic datagrid. The accuracy of the classifications is evaluated by cross-validation between the predicted thematic maps and the sampling and visual observations. Samples are visually described using a protocol and subsamples are analysed with a laser diffractometer. The fraction above 3 mm (i.e. gravel and shell material) is visually divided into classes. Data are combined into three major sediment classes: mud, sand, and coarse sediments.
a. Detailed metadata are provided per human activity, as well as a quality factor. b. and c. Depth recordings using multibeam technology are linked to precision positioning, making them accurate in place and space. RV Belgicas EM3002D multibeam echo sounder complies with the IHO S44 Special Order quality criteria. Under this IHO standard, the total vertical uncertainty of the depth measurements ± 0.26 m and ± 0.34 m in 10 m and 30 m water depths, respectively (within a confidence interval of ± 95%). There are yet no quality criteria for multibeam backscatter values, which means that data sets of different ships and/or different campaigns cannot be brought together in the original format. Therefore, a seabed classification is performed per dataset and afterwards the classifications are combined into one thematic datagrid. The accuracy of the classifications is evaluated by cross-validation between the predicted thematic maps and the sampling and visual observations. Samples are visually described using a protocol and subsamples are analysed with a laser diffractometer. The fraction above 3 mm (i.e. gravel and shell material) is visually divided into classes. Data are combined into three major sediment classes: mud, sand, and coarse sediments.
a. Detailed metadata are provided per human activity, as well as a quality factor. b. and c. Depth recordings using multibeam technology are linked to precision positioning, making them accurate in place and space. RV Belgicas EM3002D multibeam echo sounder complies with the IHO S44 Special Order quality criteria. Under this IHO standard, the total vertical uncertainty of the depth measurements ± 0.26 m and ± 0.34 m in 10 m and 30 m water depths, respectively (within a confidence interval of ± 95%). There are yet no quality criteria for multibeam backscatter values, which means that data sets of different ships and/or different campaigns cannot be brought together in the original format. Therefore, a seabed classification is performed per dataset and afterwards the classifications are combined into one thematic datagrid. The accuracy of the classifications is evaluated by cross-validation between the predicted thematic maps and the sampling and visual observations. Samples are visually described using a protocol and subsamples are analysed with a laser diffractometer. The fraction above 3 mm (i.e. gravel and shell material) is visually divided into classes. Data are combined into three major sediment classes: mud, sand, and coarse sediments.
a. Detailed metadata are provided per human activity, as well as a quality factor. b. and c. Depth recordings using multibeam technology are linked to precision positioning, making them accurate in place and space. RV Belgicas EM3002D multibeam echo sounder complies with the IHO S44 Special Order quality criteria. Under this IHO standard, the total vertical uncertainty of the depth measurements ± 0.26 m and ± 0.34 m in 10 m and 30 m water depths, respectively (within a confidence interval of ± 95%). There are yet no quality criteria for multibeam backscatter values, which means that data sets of different ships and/or different campaigns cannot be brought together in the original format. Therefore, a seabed classification is performed per dataset and afterwards the classifications are combined into one thematic datagrid. The accuracy of the classifications is evaluated by cross-validation between the predicted thematic maps and the sampling and visual observations. Samples are visually described using a protocol and subsamples are analysed with a laser diffractometer. The fraction above 3 mm (i.e. gravel and shell material) is visually divided into classes. Data are combined into three major sediment classes: mud, sand, and coarse sediments.
The laboratory procedure for analysing macrobenthic samples is since 24/05/2011 accredited under the BELAC ISO17025 norm (ILVO-DIER-ANIMALAB; CertificaatNr: BELAC T-315). The lab take also part in the benthos module of the NMBAQCS programme (www.nmbaqcs.org).
The laboratory procedure for analysing macrobenthic samples is since 24/05/2011 accredited under the BELAC ISO17025 norm (ILVO-DIER-ANIMALAB; CertificaatNr: BELAC T-315). The lab take also part in the benthos module of the NMBAQCS programme (www.nmbaqcs.org).
The laboratory procedure for analysing macrobenthic samples is since 24/05/2011 accredited under the BELAC ISO17025 norm (ILVO-DIER-ANIMALAB; CertificaatNr: BELAC T-315). The lab take also part in the benthos module of the NMBAQCS programme (www.nmbaqcs.org).
Unknown
Unknown
Unknown
Unknown
Reference collections are used and experts are consulted if necessary.
Reference collections are used and experts are consulted if necessary.
Reference collections are used and experts are consulted if necessary.
Collection of replicate samples for Hammon grabs.
Collection of replicate samples for Hammon grabs.
Data management
a. Results of the geographic data analysis are stored in GIS files b. and c. Once the methodology has been fully developed, the data and metadata will be made available to BMDC, which will make it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
a. Results of the geographic data analysis are stored in GIS files b. and c. Once the methodology has been fully developed, the data and metadata will be made available to BMDC, which will make it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
a. Results of the geographic data analysis are stored in GIS files b. and c. Once the methodology has been fully developed, the data and metadata will be made available to BMDC, which will make it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
a. Results of the geographic data analysis are stored in GIS files b. and c. Once the methodology has been fully developed, the data and metadata will be made available to BMDC, which will make it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
Data is reported and archived in EuroOBIS and GBIF via EMODNET-Biology after each permit reporting period. The data is also transferred to BMDC, which makes it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
Data is reported and archived in EuroOBIS and GBIF via EMODNET-Biology after each permit reporting period. The data is also transferred to BMDC, which makes it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
Data is reported and archived in EuroOBIS and GBIF via EMODNET-Biology after each permit reporting period. The data is also transferred to BMDC, which makes it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
Data is reported and archived in EuroOBIS and GBIF via EMODNET-Biology after each permit reporting period. The data is also transferred to BMDC, which makes it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
Data is reported and archived in EuroOBIS and GBIF via EMODNET-Biology after each permit reporting period. The data is also transferred to BMDC, which makes it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
Data is reported and archived in EuroOBIS and GBIF via EMODNET-Biology after each permit reporting period. The data is also transferred to BMDC, which makes it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
Data is reported and archived in EuroOBIS and GBIF via EMODNET-Biology after each permit reporting period. The data is also transferred to BMDC, which makes it publicly accessible via the RBINS metadata catalogue (http://metadata.naturalsciences.be).
The data is transmitted via BMDC's Data Tracking System, which makes it publicly accessible via RBINS' metadata catalogue (http://metadata.naturalsciences.be).
The data is transmitted via BMDC's Data Tracking System, which makes it publicly accessible via RBINS' metadata catalogue (http://metadata.naturalsciences.be).
The data is transmitted via BMDC's Data Tracking System, which makes it publicly accessible via RBINS' metadata catalogue (http://metadata.naturalsciences.be).
The data is transmitted via BMDC's Data Tracking System, which makes it publicly accessible via RBINS' metadata catalogue (http://metadata.naturalsciences.be).
The data is transmitted via BMDC's Data Tracking System, which makes it publicly accessible via RBINS' metadata catalogue (http://metadata.naturalsciences.be).
Data access
Related indicator/name
Contact
Vera Van Lancker, Royal Belgian Institute of Natural Science (RBINS)
Vera Van Lancker, Royal Belgian Institute of Natural Science (RBINS)
Vera Van Lancker, Royal Belgian Institute of Natural Science (RBINS)
Vera Van Lancker, Royal Belgian Institute of Natural Science (RBINS)
Gert Van Hoey, Institute for Agriculture, Fishery and Food research (ILVO)
Gert Van Hoey, Institute for Agriculture, Fishery and Food research (ILVO)
Gert Van Hoey, Institute for Agriculture, Fishery and Food research (ILVO)
Gert Van Hoey, Institute for Agriculture, Fishery and Food research (ILVO)
Gert Van Hoey, Institute for Agriculture, Fishery and Food research (ILVO)
Gert Van Hoey, Institute for Agriculture, Fishery and Food research (ILVO)
Gert Van Hoey, Institute for Agriculture, Fishery and Food research (ILVO)
Ulrike Braeckman, Tom Moens, Marine Biology Research Group, Ghent University
Ulrike Braeckman, Tom Moens, Marine Biology Research Group, Ghent University
Ulrike Braeckman, Tom Moens, Marine Biology Research Group, Ghent University
Giacomo Montereale Gavazzi, Royal Belgian Institute of Natural Science (RBINS)
Giacomo Montereale Gavazzi, Royal Belgian Institute of Natural Science (RBINS)
References