Member State report / Art11 / 2014 / D6 / 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 | D6 Sea-floor integrity/D1 Benthic habitats |
Member State | Denmark |
Region/subregion | Baltic Sea |
Reported by | Danish Nature Agency |
Report date | 2014-10-15 |
Report access |
http://cdr.eionet.europa.eu/dk/eu/msfd_mp/baldk/envvdzskw/BALDK-D06-04_abundance_softbottomfauna.xml
http://cdr.eionet.europa.eu/dk/eu/msfd_mp/baldk/envvdzskw/BALDK-D06-03_abundance_softbottomflora.xml
http://cdr.eionet.europa.eu/dk/eu/msfd_mp/baldk/envvdzriw/BALDK-D03-05_mortal_fisheries_porpoise.xml
http://cdr.eionet.europa.eu/dk/eu/msfd_mp/baldk/envvdzrcq/BALDK-D01-18_habitats_mammals_porpoise.xml
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Monitoring programme | Monitoring programme name | MP_D1_4_6_Mammals |
MP_D1_4_6_Mammals |
MP_D1_4_6_Mammals |
MP_D1_4_6_Mammals |
MP_D1_4_6_Mammals |
MP_D1_4_6_Mammals |
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_D7 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
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Monitoring programme | Reference existing programme | ||||||||||||||||||||||||||
Monitoring programme | Marine Unit ID |
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Q4e - Programme ID | BALDK-mammal-D01-04 |
BALDK-mammal-D01-04 |
BALDK-mammal-D01-04 |
BALDK-mammal-D01-04 |
BALDK-mammal-D01-04 |
BALDK-mammal-D01-04 |
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-D07 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
BALDK-D08 |
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Q4f - Programme description | All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable.
In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities. |
All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable.
In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities. |
All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable.
In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities. |
All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable.
In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities. |
All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable.
In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities. |
All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable.
In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities. |
"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 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, |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
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Q5e - Natural variability |
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Q5d - Adequacy for assessment of GES | Q5d - Adequate data | Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
N |
N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
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 |
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 |
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 |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Q5f - Description of programme for GES assessment |
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf.
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr.
Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016.
Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” .
DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata.
Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III).
SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
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Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf.
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr.
Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016.
Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” .
DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata.
Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III).
SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
|
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf.
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr.
Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016.
Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” .
DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata.
Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III).
SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
|
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf.
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr.
Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016.
Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” .
DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata.
Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III).
SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
|
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf.
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr.
Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016.
Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” .
DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata.
Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III).
SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
|
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf.
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr.
Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016.
Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” .
DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata.
Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III).
SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
|
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. |
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. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
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Q5g - Gap-filling date for GES assessment | By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
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_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_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_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_13_BAL DK_23_BAL DK_36_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
Q6a -Relevant targets | Q6a - Associated indicator | DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_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_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_13_BAL DK_23_BAL DK_36_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
DK_15_BAL DK_38_BAL |
Q6b - Adequacy for assessment of targets | Q6b_SuitableData | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
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 |
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 |
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 |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
|
Q6d - Description of programme for targets assessment |
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
|
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
|
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
|
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
|
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
|
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf
Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
|
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 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. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
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Q6e - Gap-filling date for targets assessment | By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
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Q6f - Plans to implement monitoring for targets assessment | |||||||||||||||||||||||||||
Q7a - Relevant activities |
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|
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Q7b - Description of monitoring of activities | The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures. |
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures. |
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures. |
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures. |
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures. |
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures. |
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 |
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. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
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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 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
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Q8a - Links to existing Monitoring Programmes |
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Reference sub-programme | Sub-programme ID | BALDK-D01-03_abundance_mammals_seals |
BALDK-D01-04_abundance_mammals_porpoise |
BALDK-D01-10_population_mammals_seals |
BALDK-D01-11_population_mammals_porpoise |
BALDK-D01-17_habitats_mammals_seals |
BALDK-D01-18_habitats_mammals_porpoise |
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-D08-01_health_birds_breeding |
BALDK-D08-02_health_fish_demersal |
BALDK-D08-03_health_fish_commercial |
BALDK-D08-06_health_fish_coastal |
BALDK-D08-09_mortality_birds |
BALDK-D08-10_health_hardbottomfauna |
BALDK-D08-12_health_softbottomfauna |
BALDK-D08-13_CONTAMIN_input_atmos |
BALDK-D08-14_CONTAMIN_INPUT_point_sources |
BALDK-D08-17_CONTAMIN_water |
BALDK-D08-18_CONTAMIN_sediment |
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Reference sub-programme | Sub-programme name | Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Mobile species - population characteristics |
Mobile species - state of habitats |
Mobile species - state of habitats |
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 |
Activities extracting non-living resources (sand, gravel, dredging) |
Contaminant levels - in species, including seafood |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Benthic species - health status |
Benthic species - health status |
Contaminant inputs - from atmosphere |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Q4g - Sub-programmes | Sub-programme ID | BALDK-D01-03_abundance_mammals_seals |
BALDK-D01-04_abundance_mammals_porpoise |
BALDK-D01-10_population_mammals_seals |
BALDK-D01-11_population_mammals_porpoise |
BALDK-D01-17_habitats_mammals_seals |
BALDK-D01-18_habitats_mammals_porpoise |
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-D08-01_health_birds_breeding |
BALDK-D08-02_health_fish_demersal |
BALDK-D08-03_health_fish_commercial |
BALDK-D08-06_health_fish_coastal |
BALDK-D08-09_mortality_birds |
BALDK-D08-10_health_hardbottomfauna |
BALDK-D08-12_health_softbottomfauna |
BALDK-D08-13_CONTAMIN_input_atmos |
BALDK-D08-14_CONTAMIN_INPUT_point_sources |
BALDK-D08-17_CONTAMIN_water |
BALDK-D08-18_CONTAMIN_sediment |
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Q4g - Sub-programmes | Sub-programme name | Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Mobile species - population characteristics |
Mobile species - state of habitats |
Mobile species - state of habitats |
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 |
Activities extracting non-living resources (sand, gravel, dredging) |
Contaminant levels - in species, including seafood |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Benthic species - health status |
Benthic species - health status |
Contaminant inputs - from atmosphere |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Q4k - Monitoring purpose | StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
Activities |
StateImpact |
StateImpact |
Activities |
StateImpact |
StateImpact |
Pressurse |
Pressurse |
Pressurse Measures |
Pressurse |
Pressurse |
Pressurse Measures |
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Q4l - Links of monitoring programmes of other Directives and Conventions | Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
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. |
http://www.vildtsundhed.dk/english/Activities/Surveillance
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The international coordinated trawl surveys are directed to the demersal species i.e. cod and flounder and other flatfishes in the Baltic Sea, however in the recent years other species are also intensively investigated to support ecosystem analyses. The survey is part of the Danish DCF covered under the CFP. |
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. |
NOVANA
OSPAR CEMP
HELCOM COMBINE
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http://naturstyrelsen.dk/naturoplevelser/jagt/tilskadekommet-vildt/beredskabsplan-for-havpattedyr-og-havfugle/ http://naturstyrelsen.dk/media/nst/Attachments/Beredskabsplanforhavpattedyrmarts2012.pdf
There is established a contingency plan designed to ensure a coordinated and effective action on marine mammals and seabirds in an emergency or in case of strandings in the country.
An effective contingency plan is an important prerequisite for being able to take steps to mitigate or avert the effects of, for example, an oil disaster at sea or deaths of marine mammals.
The Danish contingency plan for marine mammals and seabirds have two main functions: 1) to build a knowledge base that makes it possible to prevent and 2) to monitor an evolving situation and take the necessary measures so that the sick, stranded and oil-contaminated animals do not suffer unnecessarily. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.3 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.10 and 8.11 shows the position of the stations. 50% of the stations are in the BALDK area and 50% 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/vandmiljoe/overvaagning-af-vand-og-natur/
Table 8.3 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.10 and 8.11 shows the position of the stations. 50% of the stations are in the BALDK area and 50% 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, Seafood Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
The Danish monitoring program for air quality and atmospheric deposition contrubutes to the following other programmes: The EMEP monitoring program under CLRTAP, OSPAR, PARCOM and the monitoring in relation to the EU air quality directive (2008/50/EC). |
Water framework directive
IPPC-directive
COUNCIL DIRECTIVE of 4 May 1976 on pollution caused by certain dangerous substances discharged into the aquatic environment of the Community (76/464/EEC)
OSPAR
HELCOM
Stockholmkonvention
The strategy in the monitoring programme is meeting of all obligations and needs within the same programme if possible. |
NOVA national monitoring program, Bay of Aarhus.
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NOVANA
OSPAR CEMP
HELCOM COMBINE
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Q5c - Features | Q5c - Habitats |
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Q5c - Features | Q5c - Species list |
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Q5c - Features | Q5c - Physical/Chemical features |
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Q5c - Features | Q5c - Pressures |
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Q9a - Elements |
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Q5a - GES criteria | Relevant GES criteria |
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Q5b - GES indicators | Relevant GES indicators |
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Q9b - Parameters monitored (state/impact) | Species distribution |
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Q9b - Parameters monitored (state/impact) | Species population size |
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Q9b - Parameters monitored (state/impact) | Species population characteristics |
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Q9b - Parameters monitored (state/impact) | Species impacts |
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Q9b - Parameters monitored (state/impact) | Habitat distribution |
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Q9b - Parameters monitored (state/impact) | Habitat extent |
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Q9b - Parameters monitored (state/impact) | Habitat condition (physical-chemical) |
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Q9b - Parameters monitored (state/impact) | Habitat condition (biological) |
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Q9b - Parameters monitored (state/impact) | Habitat impacts |
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Q9b - Parameters monitored (pressures) | Pressure input |
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Q9b - Parameters monitored (pressures) | Pressure output |
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Q9b - Parameters monitored (activity) | Activity |
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Q9b Parameters monitored (other) | Other |
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Q41 Spatial scope | MSland_FW |
WFD_CW TerritorialWaters EEZ |
MSland_FW |
WFD_TW WFD_CW TerritorialWaters |
MSland_FW |
WFD_CW TerritorialWaters |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
WFD_CW |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
EEZ BeyondMSwaters |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW |
MSland_FW WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW |
WFD_CW |
WFD_CW TerritorialWaters EEZ |
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Q4j - Description of spatial scope | Harbour seals monitored since 1979.
Grey seals monitored since 2011.
All sites where seals go on land are included in the program. |
Harbour porpoises occur in all Danish waters. Every 5-6th year an international survey (mini-SCANS+SCANS) conduct an abundacea survey covering this region except for Bornholm waters. For Bornholm waters a new method using acoustic data loggers have been developed (SAMBAH), but is not yet part of the national monitoring program. |
In Danish waters there is 4 populations of harbour seals and 2 populations of grey seals. In this region both the Kattegat and western Baltic harbour seal population is shared with Sweden. The Baltic grey seal population is shared with Sweden, Finland and Estonia. |
Denmark share 3 harbour porpoise poulations with the North Sea ranage states (North Sea population), Sweden and Germany (Belt Sea population) and the Baltic proper range states (Baltic population). The Baltic Sea poulation and half of the Belt Sea population is living within the BALDK region |
Harbour seals monitored since 1979.
Grey seals monitored since 2011.
All land sites are monitored but there is no program covering the marine part of the seals's habitat. |
All major Natura2000 sites within this region is monitored. |
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. |
Wildlifehealth.dk survey the health status of the Danish wildlife continuously. The surveillance consist of both active and passive (necropsy of dead game submitted to Wildlifehealth.dk) and active (sampled on purpose to establish the health status of the species in a region) surveillance. Information from both surveillance programmes are used for research. |
BITS is an international ICES coordinated survey, were Denmark gets appointed stations in Danish EZ zone as well as in international water in the Baltic. For every survey conducted a new list of stations is appointed and the area covered can vary between surveys. However, as a standard Denmark is conducting 18*2 days survey each year and this corresponds to 50 fishing stations and 80 plankton stations in the 1st quarter and similar in the 4th quarter survey. An international ICES manual is followed and a link to the newest version is added. DTU Aqua is participating in the ICES group (WGBIFS) coordinating the survey.
http://www.ices.dk/marine-data/Documents/DATRAS%20Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf |
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. |
In representative coastal areas, coordinated with the monitoring activities on contaminnant levels in fish. |
All coastal areas
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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 program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/vandmiljoe/overvaagning-af-vand-og-natur/
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 Danish monitoring program for air quality and depositons is based on a few coastal fixed measurements stations where concentrations in air and wetdeposition is measured. The results from these measurements is in a simple way extrapolateed to cover the Danish land areas and the inner Danish waters. For organic cantaminants only measurents of wet deposition a to measurements sites is carried out. |
The programme is set up in order to cover the whole country and therefore also for the reporting area. Descibed in chap. 3 in the description of the programme: http://naturstyrelsen.dk/media/nst/Attachments/NOVANA_2del.pdf |
Transect from harbour.
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Danish parts of HELCOM convention.
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Marine Unit IDs |
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Q4h - Temporal scope | Start date- End date | 1979-9999 |
2011-9999 |
1979-9999 |
2011-9999 |
1979-9999 |
2011-9999 |
- |
- |
2011-9999 |
1990-9999 |
1987-9999 |
1990-9999 |
2005-9999 |
- |
- |
1932-9999 |
1991-9999 |
1995-9999 |
2004-9999 |
1991-9999 |
1998-9999 |
1998-9999 |
1989-9999 |
1998-9999 |
2001-2003 |
1998-9999 |
Q9h - Temporal resolution of sampling |
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Q9c - Monitoring method | The national monitoring program (NOVANA) is described (in Danish) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M16_Artsovervaagning_af_saeler.pdf |
The national monitoring program (NOVANA) is described (in Danish) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M15_Artsovervaagning_af_marsvin.pdf |
The national monitoring program (NOVANA) is described (in Dansih) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M16_Artsovervaagning_af_saeler.pdf |
The national monitoring program (NOVANA) is described (in Danish) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M15_Artsovervaagning_af_marsvin.pdf |
The national monitoring program (NOVANA) is described (in Dansih) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M16_Artsovervaagning_af_saeler.pdf |
The national monitoring program (NOVANA) is described (in Dansih) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M15_Artsovervaagning_af_marsvin.pdf |
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 |
Passive disease surveillance in collaboration between The Danish Nature Agency and The National Veterinary Institute. |
ICES methods. Dioxin samples are analysed and published from DTU food. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. Other parameter measured in connection to health is condition to commarcial species. This is monitored over time to detect changes in health and growth. Furthermore, all herring aged are also analysed for the parasite nematode Anasaki in the laboratory. |
Method according to The Marine Topic Centre (M-FDC) technical guidelines (in Danish): TA M26 Biologisk effektmonitering i fisk
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M26_Biologisk_effektmonitering_i_fisk__ver_1_.pdf |
In case ofan oil spill where oiled birds are registered, the total number will be estimated and species registered. Samples of wings will be collected for age estimate http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf |
"1) OSPAR JAMP guideline on contaminant specific effects, Tecnical annex 3 on TBT-specific effects.
2) ICES TIMES guideline on lysosomal membrane stability. Both guidelines are incoorprated into the national monitoring guideline on either TBT-specific effects in marine snails and biological effects in mussels" |
"1) OSPAR JAMP guideline on contaminant specific effects, Tecnical annex 3 on TBT-specific effects
2) ICES TIMES guideline on lysosomal membrane stability. Both guidelines are incoorprated into the national monitoring guideline on either TBT-specific effects in marine snails and biological effects in mussels" |
The measurement methods are based on the methods recommended under the EMEP monitoring program. |
The samples are collected according to national technical instructions. Link to the technical instructions on sampling in the monitoring programme on point sources: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ta-for-punktkilder/. Demands for sample handling are given in special specification, which are provided by the Reference Laboratory/the Danish Nature Agency. Link to method specifikations: http://www.reference-lab.dk/metodedatablade/metodedatablade-kemiske.aspx. Demands for the analyses are found in legislation: Bekendtgørelsen om kvalitetskrav til miljømålinger nr 231 af 5. marts 2014 https://www.retsinformation.dk/Forms/R0710.aspx?id=160496. |
NOVA monitoring guidelines for NOVA 1998-2005 program.
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_8_MFS_havvand.pdf |
HELCOM (2014). Manual for marine Monitoring in the COMBINE programme of HELCOM.
http://helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual incorporated into technical annexes for the national NOVANA program |
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Q9d - Description of alteration to method | Not relevant |
Other parameter measured in connection to health is condition in the demersal species. This is monitored over time to detect changes in health. Furthermore a subset of herring is analysed for dioxin and are also are also analysed for the parasite nematode Anasaki in the laboratory. |
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Q9e - Quality assurance |
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Q9f - Quality control | OtherQC |
OtherQC |
OtherQC |
OtherQC |
OtherQC |
OtherQC |
RealandDelayedValidation |
DelayedValidation |
Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
DelayedValidation |
Unknown |
DelayedValidation |
DelayedValidation |
OtherQC |
DelayedValidation |
DelayedValidation |
DelayedValidation |
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Q9g - Spatial resolution of sampling | Q9g - Proportion of area covered % | 100 |
50 |
100 |
50 |
100 |
10 |
100 |
2 |
50 |
100 |
90 |
90 |
90 |
100 |
10 |
50 |
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Q9g - Spatial resolution of sampling | Q9g - No. of samples | For the Belt Sea area it is 1/5-6 years. |
For the Belt Sea population it is 1/5-6 years. For the Baltic Sea population there is no regular schedule as the monitoring method has just been established. |
For the Natura2000 areas it is 1/3years. |
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. |
Not determined - passive sampling. |
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. |
3 |
as described above |
5 |
Measurements covers the entire callendar year. The estimated despositions for deposition to Danish land areas and Inner Dansih Waters are total annual deposition. |
2 samples/station/year
direct outlet: 12 stations
indirect outlet: 9 stations |
4 |
10 |
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Q9i - Description of sample representivity | variation in relation to risk across the area |
The stations are for most parts used to give a spatial more than time-trend view of concentrations/pressures within different marine areas. Some stations are analysed in duplicates from two subsamples at the same location, others are sampled within the same area in relative close proximity to give an estimate of the area variance. |
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Q10a - Scale for aggregation of data |
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Q10b - Other scale for aggregation of data | The abundance of harbour seals should be aggregated in the four Danish management units. For this region the Kattegat (partly covering region ANSDK and shared with Sweden) and the Western Baltic also shared with Sweden. For the grey seals the Dniah counts should be part of the count for all of the Baltic Sea. |
Porpoise abundance should be aggregated on population level to avoid movement between areas. For this region there is a Baltic and a Belt Sea population (expanding over both the ANSDK and BALDK). |
The population monitoring of harbour seals should be aggregated in the four Danish management units. For this region the Kattegat (partly covering region ANSDK and shared with Sweden) and the Western Baltic also shared with Sweden. For the grey seals the Dniah counts should be part of the count for all of the Baltic Sea. |
Porpoise abundance should be aggregated on population level to avoid movement between areas. For this region there is a Baltic and a Belt Sea population (expanding over both the ANSDK and BALDK) |
Each land site is monitored, but none of the marine habitats. |
Data are collected for each Natura 2000 site. |
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. |
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Q10c - Access to monitoring data | Q10c - Data type | UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData |
ProcessedData |
ProcessedData |
ProcessedData |
UnprocessedData ProcessedData |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData |
UnprocessedData |
UnprocessedData ProcessedData |
ProcessedData |
ProcessedData |
UnprocessedData ProcessedData |
UnprocessedData ProcessedData |
ProcessedData DataProducts |
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Q10c - Access to monitoring data | Q10c - Data access mechanism | LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
URLdownload |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationInternationalDC |
LocationInternationalDC |
LocationNationalDC |
URLview |
LocationNationalDC |
LocationInternationalDC |
LocationNationalDC |
LocationNationalDC |
URLview |
LocationInternationalDC |
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Q10c - Access to monitoring data | Q10c - Data access rights | Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
RestrictedSpecific |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
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Q10c - Access to monitoring data | Q10c - INSPIRE standard | OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
HabitatsBiotopes OceanographicFeatures SpeciesDistribution |
HabitatsBiotopes SeaRegions SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes OceanographicFeatures |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions |
HabitatsBiotopes SpeciesDistribution |
OceanographicFeatures SeaRegions |
OceanographicFeatures |
OceanographicFeatures SeaRegions |
HabitatsBiotopes OceanographicFeatures |
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Q10c - Access to monitoring data | Q10c Date data are available | 2014-11 |
2014-11 |
2014-11 |
2014-11 |
2014-11 |
2014-11 |
2014-12 |
2015-04 |
2015-04 |
2015-04 |
2014-10 |
2014-12 |
2015-04 |
2015-04 |
2014-12 |
2015-12 |
2015-04 |
2015-04 |
1990-01 |
2014-12 |
2014-12 |
1999-01 |
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Q10c - Access to monitoring data | Q10c - Data update frequency | Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
2yearly |
3monthly |
Yearly |
Yearly |
Yearly |
Yearly |
Asneeded |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
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Q10d - Description of data access | 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 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 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 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 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 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. |
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 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. |
In ICES DATRAS database. In addition, aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB). In addition, aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
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. |
Aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
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. |
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. |
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. |
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 will be reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA and in the forthcoming MSFD article 8 initial assessment in 2018 |
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. |