Member State report / Art11 / 2014 / D3 / Denmark / Baltic Sea

Report type Member State report to Commission
MSFD Article Art. 11 Monitoring programmes (and Art. 17 updates)
Report due 2014-10-15
GES Descriptor D3 Commercial fish and shellfish
Member State Denmark
Region/subregion Baltic Sea
Reported by Danish Nature Agency
Report date 2014-10-15
Report access
Monitoring programme Monitoring programme name
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D3
MP_D3
MP_D3
MP_D3
MP_D3
MP_D7
Monitoring programme Reference existing programme
Monitoring programme Marine Unit ID
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
Q4e - Programme ID
BALDK-D01,04,06
BALDK-D01,04,06
BALDK-D01,04,06
BALDK-D01,04,06
BALDK-D01,04,06
BALDK-D01,04,06
BALDK-D01,04,06
BALDK-D03
BALDK-D03
BALDK-D03
BALDK-D03
BALDK-D03
BALDK-D07
Q4f - Programme description
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework: • State of habitats (habitat for species, extent, suitability) • Mortality rates from anthropogenic activities • Distribution and extent (incl. habitat forming species and biogenic reefs) • Physical characteristics (topography, bathymetry, organics, oxygen levels) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from bottom trawling • Extracting non-living ressources
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework: • State of habitats (habitat for species, extent, suitability) • Mortality rates from anthropogenic activities • Distribution and extent (incl. habitat forming species and biogenic reefs) • Physical characteristics (topography, bathymetry, organics, oxygen levels) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from bottom trawling • Extracting non-living ressources
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework: • State of habitats (habitat for species, extent, suitability) • Mortality rates from anthropogenic activities • Distribution and extent (incl. habitat forming species and biogenic reefs) • Physical characteristics (topography, bathymetry, organics, oxygen levels) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from bottom trawling • Extracting non-living ressources
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework: • State of habitats (habitat for species, extent, suitability) • Mortality rates from anthropogenic activities • Distribution and extent (incl. habitat forming species and biogenic reefs) • Physical characteristics (topography, bathymetry, organics, oxygen levels) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from bottom trawling • Extracting non-living ressources
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework: • State of habitats (habitat for species, extent, suitability) • Mortality rates from anthropogenic activities • Distribution and extent (incl. habitat forming species and biogenic reefs) • Physical characteristics (topography, bathymetry, organics, oxygen levels) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from bottom trawling • Extracting non-living ressources
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework: • State of habitats (habitat for species, extent, suitability) • Mortality rates from anthropogenic activities • Distribution and extent (incl. habitat forming species and biogenic reefs) • Physical characteristics (topography, bathymetry, organics, oxygen levels) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from bottom trawling • Extracting non-living ressources
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework: • State of habitats (habitat for species, extent, suitability) • Mortality rates from anthropogenic activities • Distribution and extent (incl. habitat forming species and biogenic reefs) • Physical characteristics (topography, bathymetry, organics, oxygen levels) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from bottom trawling • Extracting non-living ressources
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.
The oceanographical monitoring programme of the Danish Meteorological Institute, DMI measures water level, tides, water temperature and currents that provide data for the forecast models of the DMI institute. The data supplements the general marine data collected in the framework of the existing environmental monitoring and is included in the marine models being developed under the National Monitoring Programme for Water and Nature, NOVANA. In the present BALDK-D07 programme on hydrological changes extraction operations are included as these may cause hydrographical changes. Major infrastructure works such as the fortcoming fixed link between Denmark and Germany is not included in the MSFD programme. A separate programme will be developed to control and monitor environmental status in relation to the environmental targets stipulated in the forthcoming Construction Bill for the fixed link across Fehmarn,
Q5e - Natural variability
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Qualitative
  • Quantiative
Q5d - Adequacy for assessment of GES Q5d - Adequate data
N
N
N
N
N
N
N
Y
Y
Y
Y
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Established methods
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate understanding of GES
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate capacity
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5f - Description of programme for GES assessment
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
According to coordination in ICES
According to coordination in ICES
According to coordination in ICES
According to coordination in ICES
According to coordination in ICES
The general programme provides information to assess possible alternations og the physical environment. Th extration activity is regulated in detail in Statutory Order no. 1169 issued 3/10-2013. In addition to this separate programmes are prepared in relation to possible large scale construction activities at sea based on EIA-assessments.
Q5g - Gap-filling date for GES assessment
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q5h - Plans to implement monitoring for GES assessment
Q6a -Relevant targets Q6a - Environmental target
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_13_BAL DK_23_BAL DK_36_BAL
Q6a -Relevant targets Q6a - Associated indicator
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL
DK_13_BAL DK_23_BAL DK_36_BAL
Q6b - Adequacy for assessment of targets Q6b_SuitableData
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6b - Adequacy for assessment of targets Q6b_EstablishedMethods
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6b - Adequacy for assessment of targets Q6d_AdequateCapacity
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6c - Target updating
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6d - Description of programme for targets assessment
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 7. Togehter with existing data series information on variability, trends and distances from levels recorded previously the programme will provide data for assessing possible progress towards reaching targets.
Q6e - Gap-filling date for targets assessment
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q6f - Plans to implement monitoring for targets assessment
Q7a - Relevant activities
  • Dredging
  • MiningSandGravel
  • Dredging
  • MiningSandGravel
  • Dredging
  • MiningSandGravel
  • Dredging
  • MiningSandGravel
  • Dredging
  • MiningSandGravel
  • Dredging
  • MiningSandGravel
  • Dredging
  • MiningSandGravel
  • Fisheries
  • SeaweedOtherSeafood
  • Fisheries
  • SeaweedOtherSeafood
  • Fisheries
  • SeaweedOtherSeafood
  • Fisheries
  • SeaweedOtherSeafood
  • Fisheries
  • SeaweedOtherSeafood
  • CablesPipelines
  • Dredging
  • LandClaimDefence
  • MiningSandGravel
Q7b - Description of monitoring of activities
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed
According to guidelines of ICES agreements
According to guidelines of ICES agreements
According to guidelines of ICES agreements
According to guidelines of ICES agreements
According to guidelines of ICES agreements
The programme provides data on key hydrological indicators including pressures impacting the hydrological quality. Extraction of nonliving ressources is regulated in detail in Staturoy Order no. 1169 issued 3/10-2013.
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
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q8a - Links to existing Monitoring Programmes
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • WFD
  • CFP-DC-MAP
  • CFP-DC-MAP
  • CFP-DC-MAP
  • CFP-DC-MAP
  • CFP-DC-MAP
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • WFD
Reference sub-programme Sub-programme ID
BALDK-D01-22_seabed_distribution
BALDK-D06-02_abundance_hardbottom
BALDK-D06-03_abundance_softbottomflora
BALDK-D06-04_abundance_softbottomfauna
BALDK-D06-06_physidisturb_trawl
BALDK-D03-04_mortal_fisheries_birds
BALDK-D03-05_mortal_fisheries_porpoise
BALDK-D03-06_mortal_fisheries_seals
BALDK-D03-08_mortal_fish_coastal
BALDK-D03-10_mortal_fish_offsh_commercial
Reference sub-programme Sub-programme name
Seabed habitats - community characteristics
Physical disturbance - from dredging and disposal of dredged material
Seabed habitats - physical/chemical characteristics
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Physical disturbance - from bottom trawling
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Activities extracting non-living resources (sand, gravel, dredging)
Q4g - Sub-programmes Sub-programme ID
BALDK-D01-22_seabed_distribution
BALDK-D06-02_abundance_hardbottom
BALDK-D06-03_abundance_softbottomflora
BALDK-D06-04_abundance_softbottomfauna
BALDK-D06-06_physidisturb_trawl
BALDK-D03-04_mortal_fisheries_birds
BALDK-D03-05_mortal_fisheries_porpoise
BALDK-D03-06_mortal_fisheries_seals
BALDK-D03-08_mortal_fish_coastal
BALDK-D03-10_mortal_fish_offsh_commercial
Q4g - Sub-programmes Sub-programme name
Seabed habitats - community characteristics
Physical disturbance - from dredging and disposal of dredged material
Seabed habitats - physical/chemical characteristics
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Physical disturbance - from bottom trawling
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Activities extracting non-living resources (sand, gravel, dredging)
Q4k - Monitoring purpose
StateImpact
StateImpact
StateImpact
StateImpact
Activities
Activities
Activities
Activities
StateImpact
Activities
Q4l - Links of monitoring programmes of other Directives and Conventions
There are no specific technical descriptions of the methods behing the distribution maps. It takes place in two phases - mapping of bottom substrates using either side scan sonar or multibeam sonar and surveys of the biological compositions of the areas using videosurveys. Definitions of the habitattypes follows a habitattype description written by the Danish Nature Agency in coorperation with DCE. http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/Biodiversitet/Habitat-beskrivelser-app4b-ver104_opdatering-havtyper2012.pdf.
Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.4 and figur 8.7 shows the position of the stations. 60% of the stations are in the BALDK area and 40% of the stations are in ANSDK area. Technical manual for the marine survey http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ . Describe the procedure for sampling in the field and the quality control of the datasets collected. The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR.
Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.3 shows the position of the stations. 70% of the stations are in the BALDK area and 30% of the stations are in ANSDK area. Technical manual for the marine survey http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ Describe the procedure for sampling in the field and the quality control of the datasets collected. The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR.
Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.5 shows the position of the stations. 60% of the stations are in the BALDK area and 40% of the stations are in ANSDK area. Technical manual for the marine survey http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ Describe the procedure for sampling in the field and the quality control of the datasets collected. The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive,Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR.
DTU Aqua has access to VMS data from all Danish commercial vessels from 2005 (above 15 meters) and from 2012 (above 12 meters). VMS data has been linked to logbook data and can therefore show pressure on the seabed by gear and target species.The access is to all Danish vessels within this size category in all waters.
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.
Catches from the recreational fisheries are registered on a voluntary basis by ”key” fishermen at fixed stations in most parts of the Danish coasts. The catches are performed with standard gillnets (one mesh size, 65 mm) and/or fyke nets, with up to 3 samples monthly in the beginning of each month, and from around April to November. Because of the mesh size used, the gillnets sample mostly adults, whereas juveniles of flounder and cod may be caught in the fyke nets. At present about 100+ fishers are invovled in the project. the last report with a detailed description can be downloaded: http://orbit.dtu.dk/files/100552186/Publishers_version.pdf
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.
Q5c - Features Q5c - Habitats
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • RedSalinity MarineCoast
  • RedSalinity MarineCoast
  • RedSalinity MarineCoast
  • RedSalinity MarineCoast
  • RedSalinity MarineCoast
  • LitSed RedSalinity
Q5c - Features Q5c - Species list
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • MammalsToothedWhales
Q5c - Features Q5c - Physical/Chemical features
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • TopographyBathymetry
Q5c - Features Q5c - Pressures
  • PhysDam_extraction
  • PhysLoss_Seal
  • PhysDam_extraction
  • PhysLoss_Seal
  • PhysDam_extraction
  • PhysLoss_Seal
  • PhysDam_extraction
  • PhysLoss_Seal
  • PhysDam_extraction
  • PhysLoss_Seal
  • PhysDam_extraction
  • PhysLoss_Seal
  • PhysDam_extraction
  • PhysLoss_Seal
  • ExtractSpeciesFishShellfish
  • Litter
  • ExtractSpeciesFishShellfish
  • Litter
  • ExtractSpeciesFishShellfish
  • Litter
  • ExtractSpeciesFishShellfish
  • Litter
  • ExtractSpeciesFishShellfish
  • Litter
  • PhysDam_extraction
Q9a - Elements
  • Sandbanks and reef distribution, type and examples of species composition within the habitats in different areas.
  • species assemblage
  • species assemblage, biomass
  • In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.
  • In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.
  • In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.
  • Most frequently occurring species in the combined database are flounder (Platichtys flesus), eel (Anguilla anguilla), eel-pout (Zoarces viviparus) and cod (Gadus morhua).
  • In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.
Q5a - GES criteria Relevant GES criteria
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 1.1
  • 1.2
  • 1.3
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 1.1
  • 1.2
  • 1.3
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 1.1
  • 1.2
  • 1.3
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 1.1
  • 1.2
  • 1.3
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 1.6
  • 3.1
  • 4.3
  • 7.1
  • 7.2
Q5b - GES indicators Relevant GES indicators
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 1.6.3
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 7.2.2
Q9b - Parameters monitored (state/impact) Species distribution
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
Q9b - Parameters monitored (state/impact) Species population size
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
Q9b - Parameters monitored (state/impact) Species population characteristics
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
Q9b - Parameters monitored (state/impact) Species impacts
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
Q9b - Parameters monitored (state/impact) Habitat distribution
  • MP-9b-1-5-1
Q9b - Parameters monitored (state/impact) Habitat extent
  • MP-9b-1-6-1
Q9b - Parameters monitored (state/impact) Habitat condition (physical-chemical)
  • MP-9b-1-7-11
  • MP-9b-1-7-11
  • MP-9b-1-7-11
  • MP-9b-1-7-1
  • MP-9b-1-7-11
Q9b - Parameters monitored (state/impact) Habitat condition (biological)
  • MP-9b-1-8-1
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
Q9b - Parameters monitored (state/impact) Habitat impacts
  • MP-9b-1-9-2
  • MP-9b-1-9-2
  • MP-9b-1-9-2
  • MP-9b-1-9-2
Q9b - Parameters monitored (pressures) Pressure input
Q9b - Parameters monitored (pressures) Pressure output
  • MP-9b-2-2-1
Q9b - Parameters monitored (activity) Activity
  • MP-9b-3-1-1
  • MP-9b-3-1-4
  • MP-9b-3-1-1
  • MP-9b-3-1-4
  • MP-9b-3-1-1
  • MP-9b-3-1-4
  • MP-9b-3-1-1
  • MP-9b-3-1-4
Q9b Parameters monitored (other) Other
Q41 Spatial scope
WFD_TW WFD_CW TerritorialWaters EEZ
WFD_CW TerritorialWaters EEZ
WFD_CW
WFD_CW TerritorialWaters EEZ BeyondMSwaters
EEZ BeyondMSwaters
WFD_CW EEZ BeyondMSwaters
WFD_CW EEZ BeyondMSwaters
WFD_CW EEZ BeyondMSwaters
WFD_CW
WFD_CW EEZ BeyondMSwaters
Q4j - Description of spatial scope
The monitoring is not systematic. Larger scale distribution mapping of reefs and sandbanks started in 2011. Mapping takes place within Natura 2000 areas and specific mapping of deep muddy bottom and shallow mud surfaces are not mapped.
The program including rationale for the geographic scope can be found here: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions.
The program including rationale for the geographic scope can be found here: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions.
The program including rationale for the geographic scope can be found here: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions.
The vessel monitoring system (VMS) is a satellite-based monitoring system which at regular intervals provides data to the fisheries authorities on the location, course and speed of vessels.
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter. The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system.
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter. The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system.
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter. The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system.
The aim of the "Key-fishermen" projects is to register fish catches and document fish assemblages in Danish coastal waters over a consecutive number of years.
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter. The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system.
Marine Unit IDs
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
  • BAL_DK_RG_001
Q4h - Temporal scope Start date- End date
-
-
2011-9999
1990-9999
1987-9999
1990-9999
2005-9999
1995-9999
1995-9999
1995-9999
2005-9999
1995-9999
-
Q9h - Temporal resolution of sampling
  • Yearly
  • Yearly
  • 2yearly
  • Continually
  • Continually
  • Continually
  • Continually
  • Monthly
  • Continually
Q9c - Monitoring method
Methods are described in the mapping reports such as the 2011 report which can be found here: http://www2.nst.dk/Download/Udgivelser/N2000_Marin_raastof_naturtypekort_kattegat_oestersoe_2011.pdf
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del4/TA04_4_2_Haardbundsfauna.pdf
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M12_Makroalger_paa_kystnaer_haard_bund__VERSION_2_.pdf
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del4/TA04_4_1_Bloedbundsfauna.pdf
http://icesjms.oxfordjournals.org/content/68/1/245.abstract
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.
In this project 102 voluntary recreational fishermen participated, using either gillnets, fyke-nets or both gear types. Note that the results resented in this report represent catches reported by recreational fishermen. All species have caught have been registered and length measurements have been taken. The results showed a high fish biodiversity in Danish coastal waters. A total of 49 fish species were registered in gillnets and 72 in fyke-nets. This projec represent the largest and longest time series on catches in gillnets and fyke-nets along the Danish coasts. As age and length and weight by age are followed on a regular basis it is possible to follow the development over time, to estimate if the population is in a healthy state.
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.
Q9d - Description of alteration to method
Not relevant
This program is registering all birds by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch of breeding or wintering birds by is mainly registration if the bird is catch in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of birds.
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals.
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals.
The method can be seen in the manual. No age are estimated but length and weight. The data can be used to evaluate the development in the length and weight distribution for commercial species over time, as the gears are standardized.
Q9e - Quality assurance
  • Other
  • COMBINE
  • QUASIMEM
  • see link included above
  • National
  • see link included above
  • see link included above
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • National
  • ICESDataTypeGuide
Q9f - Quality control
RealandDelayedValidation
DelayedValidation
RealandDelayedValidation
RealandDelayedValidation
RealandDelayedValidation
DelayedValidation
RealandDelayedValidation
Q9g - Spatial resolution of sampling Q9g - Proportion of area covered %
2
2
2
0.3
2
Q9g - Spatial resolution of sampling Q9g - No. of samples
Sidescan data is gatherered covering most of the bottom of the mapped Natura 2000 sites. Number of videosamles vary
18% of the total vessels operating in this area were above 12 meters in 2013.
around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%. From minimum 1 station per day we sample all species with length and weight and only selected species for age.
Around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%. From minimum 1 station per day we sample all species with length and weight and only selected species for age.
Around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%. From minimum 1 station per day we sample all species with length and weight and only selected speces for age.
around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%. From minimum 1 station per day we sample all species with length and weight and only selected speces for age.
Q9i - Description of sample representivity
103 fishermen are participating with 3 sites eac. Indicating that each site represent 0.3% of the total. In total 52,000 individuals were caught in the last three year. Eelpout topped the list of species most frequently caught, mostly in fyke-nets. Next on the list was flounder with 23,000 individuals being caught over 3 years. An equal number of cod and eel were caught; 9,000 individuals.
Q10a - Scale for aggregation of data
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
Q10b - Other scale for aggregation of data
Currently the definitions of the habitat types are not agreed on between countries,. The definition fits within the definition described in the habitatsdirective, but could still vary from country to country. However, if other countries have similar maps produced an overall view of the the distribution of habitat types should be possible. Danish data is currently used for fisheries regulation in an international setting - where other countries have fishing rights in Danish waters.
Q10c - Access to monitoring data Q10c - Data type
ProcessedData DataProducts
ProcessedData
ProcessedData
ProcessedData
ProcessedData
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData
ProcessedData DataProducts
Q10c - Access to monitoring data Q10c - Data access mechanism
URLdownload
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationInternationalDC
LocationInternationalDC
LocationInternationalDC
LocationNationalDC
LocationInternationalDC
Q10c - Access to monitoring data Q10c - Data access rights
Open
Open
Open
Open
RestrictedSpecific
Open
Open
Open
RestrictedSpecific
Open
Q10c - Access to monitoring data Q10c - INSPIRE standard
HabitatsBiotopes OceanographicFeatures SpeciesDistribution
HabitatsBiotopes SeaRegions SpeciesDistribution
HabitatsBiotopes SpeciesDistribution
HabitatsBiotopes SpeciesDistribution
HabitatsBiotopes OceanographicFeatures
OceanographicFeatures SeaRegions SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
Q10c - Access to monitoring data Q10c Date data are available
2014-12
2015-04
2015-04
2015-04
2014-10
2015-04
2015-04
2015-04
2015-10
2015-04
Q10c - Access to monitoring data Q10c - Data update frequency
Yearly
Yearly
Yearly
2yearly
3monthly
Yearly
Yearly
Yearly
Yearly
Yearly
Q10d - Description of data access
All current mapping projects has been combined: http://miljoegis.mim.dk/cbkort?&profile=natura2000planer2basis2013 Additionally the individual mapping projects are available in separat paper reports such as: http://www2.nst.dk/Download/Udgivelser/N2000_Marin_raastof_naturtypekort_kattegat_oestersoe_2011.pdfand as interactive URL sites: http://www2.naturstyrelsen.dk/habitatkortlaegning/
http://www.miljoeportal.dk/Sider/Forside.aspx, in addition aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018.
http://www.miljoeportal.dk/Sider/Forside.aspx, in addition aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018.
http://www.miljoeportal.dk/Sider/Forside.aspx. In addition, aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018.
Data is available and can be requested. As both logbook data and VMS data is realtime and online the data can be made available on request. Do to the law on personal data, the data is only made available in aggregated form. In addition, aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018.
In ICES Regional data base (RDB), as well as in the forthcoming MSFD art 8 initial assessment due in 2018.
In ICES Regional data base (RDB) as well as in the forthcoming MSFD art 8 initial assessment due in 2018..
In ICES Regional data base (RDB) as well as in the forthcoming MSFD art 8 initial assessment due in 2018.
A national data base is holding the data, as well as in the forthcoming MSFD art 8 initial assessment due in 2018.
In ICES Regional data base (RDB).as well as in the forthcoming MSFD art 8 initial assessment due in 2018.