Member State report / Art11 / 2014 / D1-C / 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 | D1 Cephalopods |
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_Birds |
MP_D1_4_6_Birds |
MP_D1_4_6_Birds |
MP_D1_4_6_Birds |
MP_D1_4_6_Birds |
MP_D1_4_6_Birds |
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_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D5 |
MP_D5 |
MP_D5 |
MP_D5 |
MP_D5 |
MP_D5 |
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-birds-D01-04 |
BALDK-birds-D01-04 |
BALDK-birds-D01-04 |
BALDK-birds-D01-04 |
BALDK-birds-D01-04 |
BALDK-birds-D01-04 |
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-D03 |
BALDK-D03 |
BALDK-D03 |
BALDK-D03 |
BALDK-D03 |
BALDK-D05 |
BALDK-D05 |
BALDK-D05 |
BALDK-D05 |
BALDK-D05 |
BALDK-D05 |
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 | Birds are generally well monitored in danish waters. The programme includes state/impact, pressures, activities and measures. Marine birds are primerely monitored as a functional group in MSFD context. All birds directive areas and other baltic sea areas are monitored. Monitoring is primerely focused on state (numbers and distribution). In case of relevant populations not beeing stabile or in progress further investigative monitoring will be initiated to identify causalities. |
Birds are generally well monitored in danish waters. The programme includes state/impact, pressures, activities and measures. Marine birds are primerely monitored as a functional group in MSFD context. All birds directive areas and other baltic sea areas are monitored. Monitoring is primerely focused on state (numbers and distribution). In case of relevant populations not beeing stabile or in progress further investigative monitoring will be initiated to identify causalities. |
Birds are generally well monitored in danish waters. The programme includes state/impact, pressures, activities and measures. Marine birds are primerely monitored as a functional group in MSFD context. All birds directive areas and other baltic sea areas are monitored. Monitoring is primerely focused on state (numbers and distribution). In case of relevant populations not beeing stabile or in progress further investigative monitoring will be initiated to identify causalities. |
Birds are generally well monitored in danish waters. The programme includes state/impact, pressures, activities and measures. Marine birds are primerely monitored as a functional group in MSFD context. All birds directive areas and other baltic sea areas are monitored. Monitoring is primerely focused on state (numbers and distribution). In case of relevant populations not beeing stabile or in progress further investigative monitoring will be initiated to identify causalities. |
Birds are generally well monitored in danish waters. The programme includes state/impact, pressures, activities and measures. Marine birds are primerely monitored as a functional group in MSFD context. All birds directive areas and other baltic sea areas are monitored. Monitoring is primerely focused on state (numbers and distribution). In case of relevant populations not beeing stabile or in progress further investigative monitoring will be initiated to identify causalities. |
Birds are generally well monitored in danish waters. The programme includes state/impact, pressures, activities and measures. Marine birds are primerely monitored as a functional group in MSFD context. All birds directive areas and other baltic sea areas are monitored. Monitoring is primerely focused on state (numbers and distribution). In case of relevant populations not beeing stabile or 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. |
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 programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data. |
The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data. |
The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data. |
The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data. |
The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data. |
The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data. |
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 |
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 |
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 |
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 |
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 |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Q5f - Description of programme for GES assessment |
Link NOVANA.
Jagtstatistikker
Fugle-entusiaster indrapporterer observationer af fugle i en on-line database DOF-basen. Data dækker lokaliteter over hele landet, men med sparsom dækning på det marine område. Kystnære lokaliteter er derimod vel-repræsenterede.
DTU Aqua forvalter et program med ca. 100 ”Nøglefiskere” i 18 kystnære lokaliteter, hvor der anvendes standardiserede ruser og garn. Der gennemføres primært overvågning af kystnære fisk, men også fugle og anden utilsigtet bifangst.
DTU-Aqua har et projekt, hvor bifangst af både fugle og marsvin rapporteres vha. video-overvågning af kutternes garn-ophaling.
Desuden kommer der informationer om bifangster af fugle i fiskeredskaber fra et projekt som Naturerhvervstyrelsen kører med AU omkring fritids-fiskeriet. Projektet fokuserer på Fuglebeskyttelsesområder i Aalborg Bugt og i Det sydfynske Øhav.
Endelig er det et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Naturstyrelsen har udarbejdet beredskabsplan (1997) for både havpattedyr og –fugle, som stadig gælder for fuglene: http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf . Formålet er bl.a. at indsamle informationer om olieindsmurte fugle herunder populationsstatus mm.
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Link NOVANA.
Jagtstatistikker
Fugle-entusiaster indrapporterer observationer af fugle i en on-line database DOF-basen. Data dækker lokaliteter over hele landet, men med sparsom dækning på det marine område. Kystnære lokaliteter er derimod vel-repræsenterede.
DTU Aqua forvalter et program med ca. 100 ”Nøglefiskere” i 18 kystnære lokaliteter, hvor der anvendes standardiserede ruser og garn. Der gennemføres primært overvågning af kystnære fisk, men også fugle og anden utilsigtet bifangst.
DTU-Aqua har et projekt, hvor bifangst af både fugle og marsvin rapporteres vha. video-overvågning af kutternes garn-ophaling.
Desuden kommer der informationer om bifangster af fugle i fiskeredskaber fra et projekt som Naturerhvervstyrelsen kører med AU omkring fritids-fiskeriet. Projektet fokuserer på Fuglebeskyttelsesområder i Aalborg Bugt og i Det sydfynske Øhav.
Endelig er det et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Naturstyrelsen har udarbejdet beredskabsplan (1997) for både havpattedyr og –fugle, som stadig gælder for fuglene: http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf . Formålet er bl.a. at indsamle informationer om olieindsmurte fugle herunder populationsstatus mm.
|
Link NOVANA.
Jagtstatistikker
Fugle-entusiaster indrapporterer observationer af fugle i en on-line database DOF-basen. Data dækker lokaliteter over hele landet, men med sparsom dækning på det marine område. Kystnære lokaliteter er derimod vel-repræsenterede.
DTU Aqua forvalter et program med ca. 100 ”Nøglefiskere” i 18 kystnære lokaliteter, hvor der anvendes standardiserede ruser og garn. Der gennemføres primært overvågning af kystnære fisk, men også fugle og anden utilsigtet bifangst.
DTU-Aqua har et projekt, hvor bifangst af både fugle og marsvin rapporteres vha. video-overvågning af kutternes garn-ophaling.
Desuden kommer der informationer om bifangster af fugle i fiskeredskaber fra et projekt som Naturerhvervstyrelsen kører med AU omkring fritids-fiskeriet. Projektet fokuserer på Fuglebeskyttelsesområder i Aalborg Bugt og i Det sydfynske Øhav.
Endelig er det et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Naturstyrelsen har udarbejdet beredskabsplan (1997) for både havpattedyr og –fugle, som stadig gælder for fuglene: http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf . Formålet er bl.a. at indsamle informationer om olieindsmurte fugle herunder populationsstatus mm.
|
Link NOVANA.
Jagtstatistikker
Fugle-entusiaster indrapporterer observationer af fugle i en on-line database DOF-basen. Data dækker lokaliteter over hele landet, men med sparsom dækning på det marine område. Kystnære lokaliteter er derimod vel-repræsenterede.
DTU Aqua forvalter et program med ca. 100 ”Nøglefiskere” i 18 kystnære lokaliteter, hvor der anvendes standardiserede ruser og garn. Der gennemføres primært overvågning af kystnære fisk, men også fugle og anden utilsigtet bifangst.
DTU-Aqua har et projekt, hvor bifangst af både fugle og marsvin rapporteres vha. video-overvågning af kutternes garn-ophaling.
Desuden kommer der informationer om bifangster af fugle i fiskeredskaber fra et projekt som Naturerhvervstyrelsen kører med AU omkring fritids-fiskeriet. Projektet fokuserer på Fuglebeskyttelsesområder i Aalborg Bugt og i Det sydfynske Øhav.
Endelig er det et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Naturstyrelsen har udarbejdet beredskabsplan (1997) for både havpattedyr og –fugle, som stadig gælder for fuglene: http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf . Formålet er bl.a. at indsamle informationer om olieindsmurte fugle herunder populationsstatus mm.
|
Link NOVANA.
Jagtstatistikker
Fugle-entusiaster indrapporterer observationer af fugle i en on-line database DOF-basen. Data dækker lokaliteter over hele landet, men med sparsom dækning på det marine område. Kystnære lokaliteter er derimod vel-repræsenterede.
DTU Aqua forvalter et program med ca. 100 ”Nøglefiskere” i 18 kystnære lokaliteter, hvor der anvendes standardiserede ruser og garn. Der gennemføres primært overvågning af kystnære fisk, men også fugle og anden utilsigtet bifangst.
DTU-Aqua har et projekt, hvor bifangst af både fugle og marsvin rapporteres vha. video-overvågning af kutternes garn-ophaling.
Desuden kommer der informationer om bifangster af fugle i fiskeredskaber fra et projekt som Naturerhvervstyrelsen kører med AU omkring fritids-fiskeriet. Projektet fokuserer på Fuglebeskyttelsesområder i Aalborg Bugt og i Det sydfynske Øhav.
Endelig er det et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Naturstyrelsen har udarbejdet beredskabsplan (1997) for både havpattedyr og –fugle, som stadig gælder for fuglene: http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf . Formålet er bl.a. at indsamle informationer om olieindsmurte fugle herunder populationsstatus mm.
|
Link NOVANA.
Jagtstatistikker
Fugle-entusiaster indrapporterer observationer af fugle i en on-line database DOF-basen. Data dækker lokaliteter over hele landet, men med sparsom dækning på det marine område. Kystnære lokaliteter er derimod vel-repræsenterede.
DTU Aqua forvalter et program med ca. 100 ”Nøglefiskere” i 18 kystnære lokaliteter, hvor der anvendes standardiserede ruser og garn. Der gennemføres primært overvågning af kystnære fisk, men også fugle og anden utilsigtet bifangst.
DTU-Aqua har et projekt, hvor bifangst af både fugle og marsvin rapporteres vha. video-overvågning af kutternes garn-ophaling.
Desuden kommer der informationer om bifangster af fugle i fiskeredskaber fra et projekt som Naturerhvervstyrelsen kører med AU omkring fritids-fiskeriet. Projektet fokuserer på Fuglebeskyttelsesområder i Aalborg Bugt og i Det sydfynske Øhav.
Endelig er det et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres.
Naturstyrelsen har udarbejdet beredskabsplan (1997) for både havpattedyr og –fugle, som stadig gælder for fuglene: http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf . Formålet er bl.a. at indsamle informationer om olieindsmurte fugle herunder populationsstatus mm.
|
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).
|
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. |
According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values. |
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 |
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Q5h - Plans to implement monitoring for GES assessment | |||||||||||||||||||||||||||||||||||||||||||
Q6a -Relevant targets | Q6a - Environmental target | DK_7_BAL |
DK_7_BAL |
DK_7_BAL |
DK_7_BAL |
DK_7_BAL |
DK_7_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_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_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_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_7_BAL |
DK_7_BAL |
DK_7_BAL |
DK_7_BAL |
DK_7_BAL |
DK_7_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_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_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_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 |
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 |
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 |
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 |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
|
Q6d - Description of programme for targets assessment | The programme provides data on key indicators for descriptor 1 and 4. Existing data series will enable computations on variability, trends and distances fro mlevels recorded earlier as well as provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will enable computations on variability, trends and distances fro mlevels recorded earlier as well as provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will enable computations on variability, trends and distances fro mlevels recorded earlier as well as provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will enable computations on variability, trends and distances fro mlevels recorded earlier as well as provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will enable computations on variability, trends and distances fro mlevels recorded earlier as well as provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will enable computations on variability, trends and distances fro mlevels recorded earlier as well as provide data for the assessment of possible progress towards reaching targets. |
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 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets. |
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and 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 |
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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Q7b - Description of monitoring of activities | The programme provides data on key indicators in the marine area which together with relevant pressures impact the biodiveristy and the quality of the habitats at sea. |
The programme provides data on key indicators in the marine area which together with relevant pressures impact the biodiveristy and the quality of the habitats at sea. |
The programme provides data on key indicators in the marine area which together with relevant pressures impact the biodiveristy and the quality of the habitats at sea. |
The programme provides data on key indicators in the marine area which together with relevant pressures impact the biodiveristy and the quality of the habitats at sea. |
The programme provides data on key indicators in the marine area which together with relevant pressures impact the biodiveristy and the quality of the habitats at sea. |
The programme provides data on key indicators in the marine area which together with relevant pressures impact the biodiveristy and the quality of the habitats at sea. |
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 |
According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations. |
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations. |
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations. |
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations. |
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations. |
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations. |
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 |
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By2014 |
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Q8a - Links to existing Monitoring Programmes |
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Reference sub-programme | Sub-programme ID | BALDK-D01-01_abundance_birds_breeding |
BALDK-D01-02_abundance_birds_wintering |
BALDK-D01-16_habitats_birds_wintering |
BALDK-D08-01_health_birds_breeding |
BALDK-D08-09_mortality_birds |
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-D03-04_mortal_fisheries_birds |
BALDK-D03-05_mortal_fisheries_porpoise |
BALDK-D03-06_mortal_fisheries_seals |
BALDK-D03-08_mortal_fish_coastal |
BALDK-D03-10_mortal_fish_offsh_commercial |
BALDK-D05-01_micropath_water |
BALDK-D05-02_watercolumn_physical |
BALDK-D05-03_watercolumn_chemical |
BALDK-D05-04_planktonbloom |
BALDK-D05-05_NUTRI_input_land |
BALDK-D05-06_NUTRI_input_atmos |
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 |
||||
Reference sub-programme | Sub-programme name | Mobile species - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - state of habitats |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
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 |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Microbial pathogen levels - in water column (bathing waters) |
Water column - physical characteristics |
Water column - chemical characteristics |
Plankton blooms (biomass, frequency) |
Nutrient inputs - land-based sources |
Nutrient inputs - from atmosphere |
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-D01-01_abundance_birds_breeding |
BALDK-D01-02_abundance_birds_wintering |
BALDK-D01-16_habitats_birds_wintering |
BALDK-D08-01_health_birds_breeding |
BALDK-D08-09_mortality_birds |
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-D03-04_mortal_fisheries_birds |
BALDK-D03-05_mortal_fisheries_porpoise |
BALDK-D03-06_mortal_fisheries_seals |
BALDK-D03-08_mortal_fish_coastal |
BALDK-D03-10_mortal_fish_offsh_commercial |
BALDK-D05-01_micropath_water |
BALDK-D05-02_watercolumn_physical |
BALDK-D05-03_watercolumn_chemical |
BALDK-D05-04_planktonbloom |
BALDK-D05-05_NUTRI_input_land |
BALDK-D05-06_NUTRI_input_atmos |
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 - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - state of habitats |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
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 |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Microbial pathogen levels - in water column (bathing waters) |
Water column - physical characteristics |
Water column - chemical characteristics |
Plankton blooms (biomass, frequency) |
Nutrient inputs - land-based sources |
Nutrient inputs - from atmosphere |
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 |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
Activities |
Activities |
Activities |
Activities |
StateImpact |
Activities |
Activities |
StateImpact |
StateImpact |
StateImpact |
Pressurse |
Pressurse Measures |
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 |
NOVANA - http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
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All these above activities are performed under the national Danish monitoring Program (NOVANA) as part of the national reporting to the Commission in relation to the Birds Directive. |
http://www.vildtsundhed.dk/english/Activities/Surveillance
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http://www.vildtsundhed.dk/english/Activities/Surveillance
|
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. |
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. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
Catches from the recreational fisheries are registered on a voluntary basis by ”key” fishermen at fixed stations in most parts of the Danish coasts. The catches are performed with standard gillnets (one mesh size, 65 mm) and/or fyke nets, with up to 3 samples monthly in the beginning of each month, and from around April to November. Because of the mesh size used, the gillnets sample mostly adults, whereas juveniles of flounder and cod may be caught in the fyke nets. At present about 100+ fishers are invovled in the project. the last report with a detailed description can be downloaded:
http://orbit.dtu.dk/files/100552186/Publishers_version.pdf |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
Hereby link to the EU Bathing Water Directive (Directive 2006/7/EC of 15 February 2006):
http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:064:0037:0051:EN:PDF.
Please find also link to the Danish Statutory order concerning the bathing water quality: (BEK no. 939 of 18/09/2012)
https://www.retsinformation.dk/forms/R0710.aspx?id=143189. |
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 8.1 shows the position of the stations. 63% of the stations are in the BALDK area and 37% of the stations are in ANSDK area. Also se figur 8.9 that show addition station sampeled primæry during the season where hypoxia cann occur.
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 8.1 shows the position of the stations. 63% of the stations are in the BALDK area and 37% of the stations are in ANSDK area. Also se figur 8.9 that show addition station sampeled primæry during the season where hypoxia cann occur.
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 8.6 shows the position of the stations. 33% of the stations are in the BALDK area and 67% 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. |
'HELCOM
OSPAR
Danish "Action plan against nutrient pollution of the Danish Aquatic Environment" and subsequent national action plans.
Water Framework Directive |
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). |
http://www.vildtsundhed.dk/english/Activities/Surveillance
|
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
|
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 |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW WFD_CW |
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 |
WFD_CW EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW |
WFD_CW EEZ BeyondMSwaters |
WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
MSland_FW |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
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 | For the species Sandwich Tern, Arctic Tern, Common Tern and Little Tern under the programme NOVANA:
Start date: 01-05-2006
End Date: 9999
For Great Cormorant:
Start date: 01-05-1993
End Date: 9999.
No programme for any other of the marine birds that breed in Denmark, e.g. Common Guillemot, Razorbill, Black Guillemot, Common Eider, gulls, mergansers.
In principle should all potential breeding sites of the four tern species be monitored by NOVANA, but the experience is that probably around 50-70 % of the relevant sites have been monitored by the NOVANA programme. Consequently, temporal development can be tracked for some but not all sites. |
All these above activities are performed under the national Danish monitoring Program (NOVANA) as part of the national reporting to the Commission in relation to the Birds Directive. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
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. |
All coastal areas
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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. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
The aim of the "Key-fishermen" projects is to register fish catches and document fish assemblages in Danish coastal waters over a consecutive number of years. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
This program includes the entire coastline, inland waters (estuaries) and lakes. |
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/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
The aim of the National Monitoring Programme for Water and NAture is to document the impacts of the current Programmes of Measures as well as to establish the basis for future environmental management of the Danish sea territories. |
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 programme has been established in order to document trends and inputs impacting the aquatic environment as well as to provide a basis for decision-making in relation to restore the environmental quality in freshwater and marine environment. |
The Danish monitoring program for air quality and depositons is based on a few coastal fixed measurements stations in combination with modelcalculations that cover all the Danish marins waters. The quality of the model calculations is based on comparisons with the results from the monitoring stations. |
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 | - |
1993-9999 |
2000-9999 |
1932-9999 |
1932-9999 |
1991-9999 |
1979-9999 |
2011-9999 |
1979-9999 |
2011-9999 |
1979-9999 |
2011-9999 |
- |
- |
2011-9999 |
1990-9999 |
1987-9999 |
1990-9999 |
2005-9999 |
1995-9999 |
1995-9999 |
1995-9999 |
2005-9999 |
1995-9999 |
1975-9999 |
1987-9999 |
1987-9999 |
1987-9999 |
1989-9999 |
1989-9999 |
- |
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 | For the species Sandwich Tern, Arctic Tern, Common Tern, Little Tern under the programme NOVANA (a technical description of the method exists):
The number of breeding pairs is estimated by counting the number of adults present in the colony/area of the colony and multiply this with 0.7.
This is the standard method used in the International Wadden Sea.
For Great Cormorant all occupied nests are counted at the time of season when the numbers of occupied nests are expected to be at their highest.
The person collating and writing up the data will check whether numbers reported seem reasonable and in some cases request details from the person that collected the data.
National standard: One person collates all information reported. Some of it is written up and published regularly. |
http://www.ens.dk/sites/ens.dk/files/undergrund-forsyning/vedvarende-energi/Abundance%20and%20distribution%20of%20selected%20waterbird%20species%20in%20Danish%20marine%20areas.pdf
http://www2.dmu.dk/Pub/ar261.pdf
http://www2.dmu.dk/Pub/FR606.pdf |
Passive disease surveillance in collaboration between The Danish Nature Agency and The National Veterinary Institute. |
Passive disease surveillance in collaboration between The Danish Nature Agency and The National Veterinary Institute. |
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 |
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 |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
In this project 102 voluntary recreational fishermen participated, using either gillnets, fyke-nets or both gear types. Note that the results resented in this report represent catches reported by recreational fishermen. All species have caught have been registered and length measurements have been taken. The results showed a high fish biodiversity in Danish coastal waters. A total of 49 fish species were registered in gillnets and 72 in fyke-nets. This projec represent the largest and longest time series on catches in gillnets and fyke-nets along the Danish coasts. As age and length and weight by age are followed on a regular basis it is possible to follow the development over time, to estimate if the population is in a healthy state. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
Description of the technical method is described in the Bathing Water Directive 2006/7/EC of 15 February 2006 Article 15 and must be in accordance with Annex I, IV and V in this Directive. Link enclosed:
http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:064:0037:0051:EN:PDF.
Please find also a technical description of the method described in the Danish Statutory order (Statutory Order No. 2012-09-18. 939) concerning bathing and swimming areas. Reference to chapter 2 § 4/2. Link enclosed:
https://www.retsinformation.dk/forms/R0710.aspx?id=143189.
Attached is also a general technical description of measurement methods in the Danish Statutory Order (Statutory Order No. 231 of 05/03/2014) concerning quality standards for environmental measurements:
https://www.retsinformation.dk/Forms/R0710.aspx?id=160496 |
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M03_CTD_maaling__VERSION_2_.pdf
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M04_Ilt_i_vandsoejlen.pdf
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M05_Fluorescens_ver1.pdf
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M06_Lyssvaekkelse_ver1.pdf |
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_2_vandkemi.pdf |
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_5_fytoplankton.pdf |
References: Technical guideline documents for NOVANA is available from the Danish Nature Agency (in Danish), .and Bekendtgørelse om kvalitetskrav til miljømålinger (Statutory Order on Quality requirements in environmental analyses) https://www.retsinformation.dk/Forms/R0710.aspx?id=160496 |
The measurement methods are based on the methods recommended under the EMEP monitoring program. Part of the measurement methods has been slghtly modified compared to the EMPE methods. The modifications have been documented in connection with DCE's accriditation. The model calculations is based on DCE's air quality model called Danish hemispheric eulerian model. |
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 |
This program is registering all birds by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch of breeding or wintering birds by is mainly registration if the bird is catch in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of birds. |
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals. |
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals. |
The method can be seen in the manual. No age are estimated but length and weight. The data can be used to evaluate the development in the length and weight distribution for commercial species over time, as the gears are standardized. |
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 |
Unknown |
Unknown |
Unknown |
OtherQC |
OtherQC |
OtherQC |
OtherQC |
OtherQC |
OtherQC |
RealandDelayedValidation |
DelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
DelayedValidation |
RealandDelayedValidation |
Unknown |
OtherQC |
OtherQC |
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 % | 70 |
100 |
100 |
100 |
100 |
50 |
100 |
50 |
100 |
10 |
2 |
2 |
2 |
0.3 |
2 |
100 |
100 |
2 |
50 |
100 |
90 |
90 |
90 |
100 |
10 |
50 |
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Q9g - Spatial resolution of sampling | Q9g - No. of samples | One |
Individual records of bird species and bird flocks are recorded. |
Not determined - passive sampling. |
Not determined - passive sampling. |
as described above |
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. |
around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected species for age. |
Around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected species for age. |
Around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected speces for age. |
around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected speces for age. |
840 - 1680
12-24 annual samples at each location
approx. 70 stations |
Both model calculations and measurements covers the entire callendar year. |
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 | For the species Sandwich Tern and Little Tern under the programme NOVANA: Every 3rd year.
For the species Arctic Tern and Common Tern under the programme NOVANA: Every 6th year
For Great Cormorant: Every year.
For gulls and terns in the Danish part of the Wadden Sea: Every year. |
103 fishermen are participating with 3 sites eac. Indicating that each site represent 0.3% of the total.
In total 52,000 individuals were caught in the last three year. Eelpout topped the list of species most frequently caught, mostly in fyke-nets. Next on the list was flounder with 23,000 individuals being caught over 3 years. An equal number of cod and eel were caught; 9,000 individuals. |
According to EU Directive 2006/7 / EC of 15 February 2006 on bathing water quality, sample taking will only take place in the "bathing season" (Denmark 1. of June to 1. of September / in some cases to 15. of September) and only were there are a "large number" of bathers. Link to Directive:
http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:064:0037:0051:EN:PDF.
Please find also link to the Danish Statutory order concerning bathing water:
https://www.retsinformation.dk/forms/R0710.aspx?id=143189. Please find link to the Reporting Sheet from EEA (European Environment Agency) : http://rod.eionet.europa.eu/obligations/531. |
Approx. 50% of the catchment area is covered by monitoring stations. The locations are selected mainly to cover the largest rivers and to be distributed across the entire country. The nutrient load from the remaining catchment area is estimated using models.
840 - 1680
12-24 annual samples at each location in approx. 70 stations |
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 | For terns under the NOVANA programme corrections need to be made for incomplete coverage, however, in relation to the targets of the MSFD there is no further needs. |
Can be aggregated down to very local areas, as all records are georeferenced and entered into Geodatabase. |
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 |
ProcessedData DataProducts Simulated |
UnprocessedData |
UnprocessedData ProcessedData |
UnprocessedData |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData |
ProcessedData |
ProcessedData |
ProcessedData |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData |
ProcessedData DataProducts |
UnprocessedData |
UnprocessedData |
UnprocessedData |
ProcessedData |
UnprocessedData ProcessedData |
ProcessedData Simulated |
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 |
URLview |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
URLdownload |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationInternationalDC |
LocationInternationalDC |
LocationInternationalDC |
LocationNationalDC |
LocationInternationalDC |
LocationInternationalDC |
LocationNationalDC |
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 |
Open |
Open |
Open |
Open |
Open |
RestrictedSpecific |
Open |
Open |
Open |
RestrictedSpecific |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
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Q10c - Access to monitoring data | Q10c - INSPIRE standard | HabitatsBiotopes SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
OceanographicFeatures SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
SeaRegions SpeciesDistribution |
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 |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions |
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 | 2014-12 |
2013-10 |
2014-12 |
2014-12 |
2015-12 |
2014-11 |
2014-11 |
2014-11 |
2014-11 |
2014-11 |
2014-11 |
2014-12 |
2015-04 |
2015-04 |
2015-04 |
2014-10 |
2015-04 |
2015-04 |
2015-04 |
2015-10 |
2015-04 |
2014-12 |
2014-12 |
2014-12 |
2015-04 |
2014-12 |
1990-01 |
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 |
3yearly |
Asneeded |
Yearly |
Asneeded |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
2yearly |
3monthly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
2weekly |
2weekly |
Yearly |
Yearly |
Yearly |
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. |
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. |
Aggregated data is reported 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. |
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 ICES Regional data base (RDB), as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB) as well as in the forthcoming MSFD art 8 initial assessment due in 2018.. |
In ICES Regional data base (RDB) as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
A national data base is holding the data, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB).as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is sent to the EC / EEA by the end of December each year
In addition aggregated data is reported 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. |
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. |
Aggregated data is contained in yearly progress report published 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. |
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. |