Member State report / Art11 / 2014 / D6 / Denmark / NE Atlantic: Greater North Sea

Report type Member State report to Commission
MSFD Article Art. 11 Monitoring programmes (and Art. 17 updates)
Report due 2014-10-15
GES Descriptor D6 Sea-floor integrity/D1 Benthic habitats
Member State Denmark
Region/subregion NE Atlantic: Greater North Sea
Reported by Danish Nature Agency
Report date 2014-10-15
Report access
Monitoring programme Monitoring programme name
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D7
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
MP_D8
Monitoring programme Reference existing programme
Monitoring programme Marine Unit ID
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
Q4e - Programme ID
ANSDK-mammal-D01-04
ANSDK-mammal-D01-04
ANSDK-mammal-D01-04
ANSDK-mammal-D01-04
ANSDK-mammal-D01-04
ANSDK-mammal-D01-04
ANSDK-D01,04,06
ANSDK-D01,04,06
ANSDK-D01,04,06
ANSDK-D01,04,06
ANSDK-D01,04,06
ANSDK-D01,04,06
ANSDK-D01,04,06
ANSDK-D01,04,06
ANSDK-D07
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
ANSDK-D08
Q4f - Programme description
All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is more 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. Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM
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 more 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. Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM
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 more 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. Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM
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 more 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. Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM
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 more 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. Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM
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 more 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. Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM
The monitoring programme for seabed habitats consists of about 16 subprogrammes that fulfils the main parts of the DPSIR causal framework: "Seabed habitats • Mobile species (species composition, abundance) • Mobile species population characteristics (body size, age ,sex, fecundity, mortality) • 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) • Chemical characteristics (nutrients, Oxygen, ph/CO2) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) Pressures • Physical loss –distribution and extent (infrastructure) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from sand and gravel extraction • Pysical disturbance from bottom trawling Activities • Extracting linving ressources • Extracting non-living ressources • Permanent infrastructures
The monitoring programme for seabed habitats consists of about 16 subprogrammes that fulfils the main parts of the DPSIR causal framework: "Seabed habitats • Mobile species (species composition, abundance) • Mobile species population characteristics (body size, age ,sex, fecundity, mortality) • 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) • Chemical characteristics (nutrients, Oxygen, ph/CO2) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) Pressures • Physical loss –distribution and extent (infrastructure) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from sand and gravel extraction • Pysical disturbance from bottom trawling Activities • Extracting linving ressources • Extracting non-living ressources • Permanent infrastructures
The monitoring programme for seabed habitats consists of about 16 subprogrammes that fulfils the main parts of the DPSIR causal framework: "Seabed habitats • Mobile species (species composition, abundance) • Mobile species population characteristics (body size, age ,sex, fecundity, mortality) • 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) • Chemical characteristics (nutrients, Oxygen, ph/CO2) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) Pressures • Physical loss –distribution and extent (infrastructure) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from sand and gravel extraction • Pysical disturbance from bottom trawling Activities • Extracting linving ressources • Extracting non-living ressources • Permanent infrastructures
The monitoring programme for seabed habitats consists of about 16 subprogrammes that fulfils the main parts of the DPSIR causal framework: "Seabed habitats • Mobile species (species composition, abundance) • Mobile species population characteristics (body size, age ,sex, fecundity, mortality) • 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) • Chemical characteristics (nutrients, Oxygen, ph/CO2) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) Pressures • Physical loss –distribution and extent (infrastructure) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from sand and gravel extraction • Pysical disturbance from bottom trawling Activities • Extracting linving ressources • Extracting non-living ressources • Permanent infrastructures
The monitoring programme for seabed habitats consists of about 16 subprogrammes that fulfils the main parts of the DPSIR causal framework: "Seabed habitats • Mobile species (species composition, abundance) • Mobile species population characteristics (body size, age ,sex, fecundity, mortality) • 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) • Chemical characteristics (nutrients, Oxygen, ph/CO2) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) Pressures • Physical loss –distribution and extent (infrastructure) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from sand and gravel extraction • Pysical disturbance from bottom trawling Activities • Extracting linving ressources • Extracting non-living ressources • Permanent infrastructures
The monitoring programme for seabed habitats consists of about 16 subprogrammes that fulfils the main parts of the DPSIR causal framework: "Seabed habitats • Mobile species (species composition, abundance) • Mobile species population characteristics (body size, age ,sex, fecundity, mortality) • 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) • Chemical characteristics (nutrients, Oxygen, ph/CO2) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) Pressures • Physical loss –distribution and extent (infrastructure) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from sand and gravel extraction • Pysical disturbance from bottom trawling Activities • Extracting linving ressources • Extracting non-living ressources • Permanent infrastructures
The monitoring programme for seabed habitats consists of about 16 subprogrammes that fulfils the main parts of the DPSIR causal framework: "Seabed habitats • Mobile species (species composition, abundance) • Mobile species population characteristics (body size, age ,sex, fecundity, mortality) • 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) • Chemical characteristics (nutrients, Oxygen, ph/CO2) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) Pressures • Physical loss –distribution and extent (infrastructure) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from sand and gravel extraction • Pysical disturbance from bottom trawling Activities • Extracting linving ressources • Extracting non-living ressources • Permanent infrastructures
The monitoring programme for seabed habitats consists of about 16 subprogrammes that fulfils the main parts of the DPSIR causal framework: "Seabed habitats • Mobile species (species composition, abundance) • Mobile species population characteristics (body size, age ,sex, fecundity, mortality) • 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) • Chemical characteristics (nutrients, Oxygen, ph/CO2) • Community characteristics (species composition, abundance and/or biomass) • Benthic species (species composition, abundance, coverage) Pressures • Physical loss –distribution and extent (infrastructure) • Physical loss –dredging and disposal of dredged materials • Pysical disturbance from sand and gravel extraction • Pysical disturbance from bottom trawling Activities • Extracting linving ressources • Extracting non-living ressources • Permanent infrastructures
Information on hydrological changes of watercolumn, infrastructure and recreational activities will be included in the programme at a later stage in order to render a more complete description of the main elements. However, in many of the other programmes of the MSFD information can be made available e.g. from habitatmapping, characterisitcs of the watercolumn.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework.
Q5e - Natural variability
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
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  • ExpertOpinion
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  • ExpertOpinion
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  • ExpertOpinion
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  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
Q5d - Adequacy for assessment of GES Q5d - Adequate data
Y
Y
Y
Y
Y
Y
N
N
N
N
N
N
N
N
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
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
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
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
Q5f - Description of programme for GES assessment
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry”. DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
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).
a) The programme provides data on key indicators for descriptor 1 and 4. 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.
a) The programme provides data on key indicators for descriptor 1 and 4. 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.
a) The programme provides data on key indicators for descriptor 1 and 4. 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.
a) The programme provides data on key indicators for descriptor 1 and 4. 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.
a) The programme provides data on key indicators for descriptor 1 and 4. 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.
a) The programme provides data on key indicators for descriptor 1 and 4. 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.
a) The programme provides data on key indicators for descriptor 1 and 4. 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.
a) The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
The general programme provides information to assess possible alternations og the physical environment. In addition to this separate programmes are prepared in relation to possible large scale construction activities at sea based on EIA-assessments.
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation
Q5g - Gap-filling date for GES assessment
By2014
By2014
By2014
By2014
By2014
By2014
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2014
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
Q5h - Plans to implement monitoring for GES assessment
Monitoring of benthic communites in the North Sea and Skagerrak will be started in 2015, and thus supplementing the existing monitoring programmes in the Kattegat.
Monitoring of benthic communites in the North Sea and Skagerrak will be started in 2015, and thus supplementing the existing monitoring programmes in the Kattegat.
Monitoring of benthic communites in the North Sea and Skagerrak will be started in 2015, and thus supplementing the existing monitoring programmes in the Kattegat.
Monitoring of benthic communites in the North Sea and Skagerrak will be started in 2015, and thus supplementing the existing monitoring programmes in the Kattegat.
Monitoring of benthic communites in the North Sea and Skagerrak will be started in 2015, and thus supplementing the existing monitoring programmes in the Kattegat.
Monitoring of benthic communites in the North Sea and Skagerrak will be started in 2015, and thus supplementing the existing monitoring programmes in the Kattegat.
Monitoring of benthic communites in the North Sea and Skagerrak will be started in 2015, and thus supplementing the existing monitoring programmes in the Kattegat.
Monitoring of benthic communites in the North Sea and Skagerrak will be started in 2015, and thus supplementing the existing monitoring programmes in the Kattegat.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea.
Q6a -Relevant targets Q6a - Environmental target
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_15_ANS DK_16_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_15_ANS DK_16_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_15_ANS DK_16_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_15_ANS DK_16_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_15_ANS DK_16_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_15_ANS DK_16_ANS DK_31_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_12_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_12_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_12_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_12_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_12_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_12_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_12_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_12_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_9_ANS DK_13_ANS DK_23_ANS DK_34_ANS DK_35_ANS DK_36_ANS DK_49_ANS DK_53_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
DK_15_ANS DK_26_ANS DK_38_ANS
Q6a -Relevant targets Q6a - Associated indicator
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_16_ANS DK_17_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_16_ANS DK_17_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_16_ANS DK_17_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_16_ANS DK_17_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_16_ANS DK_17_ANS DK_31_ANS
DK_1_ANS DK_2_ANS DK_5_ANS DK_6_ANS DK_8_ANS DK_16_ANS DK_17_ANS DK_31_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_4_ANS DK_9_ANS DK_11_ANS DK_13_ANS DK_20_ANS DK_22_ANS DK_24_ANS DK_25_ANS DK_35_ANS DK_36_ANS DK_47_ANS DK_48_ANS DK_49_ANS DK_50_ANS DK_51_ANS DK_52_ANS DK_53_ANS
DK_9_ANS DK_13_ANS DK_23_ANS DK_34_ANS DK_35_ANS DK_36_ANS DK_49_ANS DK_53_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
DK_15_ANS DK_38_ANS
Q6b - Adequacy for assessment of targets Q6b_SuitableData
Y
Y
Y
Y
Y
Y
N
N
N
N
N
N
N
N
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
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
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
Q6d - Description of programme for targets assessment
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 7. Togehter with existing data series information on variability, trends and distances from levels recorded previously the programme will provide data for assessing possible progress towards reaching targets.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
The 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.
Q6e - Gap-filling date for targets assessment
By2014
By2014
By2014
By2014
By2014
By2014
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
By2018
Q6f - Plans to implement monitoring for targets assessment
monitoring activities in the Skagerrak and the North Sea of seabed habitats will be extended from 2015
monitoring activities in the Skagerrak and the North Sea of seabed habitats will be extended from 2015
monitoring activities in the Skagerrak and the North Sea of seabed habitats will be extended from 2015
monitoring activities in the Skagerrak and the North Sea of seabed habitats will be extended from 2015
monitoring activities in the Skagerrak and the North Sea of seabed habitats will be extended from 2015
monitoring activities in the Skagerrak and the North Sea of seabed habitats will be extended from 2015
monitoring activities in the Skagerrak and the North Sea of seabed habitats will be extended from 2015
monitoring activities in the Skagerrak and the North Sea of seabed habitats will be extended from 2015
monitoring will be gradually phased in beginning 2014.
Q7a - Relevant activities
  • CablesPipelines
  • Dredging
  • Fisheries
  • LandClaimDefence
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • CablesPipelines
  • Dredging
  • Fisheries
  • LandClaimDefence
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • CablesPipelines
  • Dredging
  • Fisheries
  • LandClaimDefence
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • CablesPipelines
  • Dredging
  • Fisheries
  • LandClaimDefence
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • CablesPipelines
  • Dredging
  • Fisheries
  • LandClaimDefence
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • CablesPipelines
  • Dredging
  • Fisheries
  • LandClaimDefence
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • CablesPipelines
  • Dredging
  • LandClaimDefence
  • MiningSandGravel
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OilGas
  • Urban
Q7b - Description of monitoring of activities
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed.
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed.
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed.
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed.
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed.
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed.
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed.
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed.
The programme provides data on key hydrological indicators including pressures impacting the hydrological quality.
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.
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.
Q7c - Relevant measures
Q7e - Adequacy for assessment of measures Q7d - Adequate data
Q7e - Adequacy for assessment of measures Q7d - Established methods
Q7e - Adequacy for assessment of measures Q7d - Adequate understanding of GES
Q7e - Adequacy for assessment of measures Q7d - Adequate capacity
Q7e - Adequacy for assessment of measures Q7d - Addresses activities and pressures
Q7e - Adequacy for assessment of measures Q7d - Addresses effectiveness of measures
Q7d - Description of monitoring for measures
Q7f - Gap-filling date for activities and measures
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q8a - Links to existing Monitoring Programmes
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • TWSC
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • TWSC
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • TWSC
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • TWSC
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • TWSC
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • TWSC
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • OSPAR
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
  • Birds
  • HELCOM
  • Habitats
  • OSPAR
  • UWWTD
  • WFD
Reference sub-programme Sub-programme ID
ANSDK-D01-03_abundance_mammals_seals
ANSDK-D01-04_abundance_mammals_porpoise
ANSDK-D01-10_population_mammals_seals
ANSDK-D01-11_population_mammals_porpoise
ANSDK-D01-17_habitats_mammals_seals
ANSDK-D01-18_habitats_mammals_porpoise
ANSDK-D01-21_habitat_demersal_sandeel
ANSDK-D01-22_seabed_distribution
ANSDK-D06-01_seabed_community
ANSDK-D06-03_abundance_softbottomflora
ANSDK-D06-04_abundance_softbottomfauna
ANSDK-D06-06_physidisturb_trawl
ANSDK-D06-07_physidisturb_dredging
ANSDK-D07-02_ACTIVITY_nonlivingresource
ANSDK-D08-01_health_birds_breeding
ANSDK-D08-02_health_fish_demersal
ANSDK-D08-03_health_fish_commercial
ANSDK-D08-04_health_fish_sandeel
ANSDK-D08-06_health_fish_coastal
ANSDK-D08-07_health_fish_migratory
ANSDK-D08-08_health_fish_migratory_pelagic
ANSDK-D08-09_mortality_birds
ANSDK-D08-10_health_hardbottomfauna
ANSDK-D08-12_health_softbottomfauna
ANSDK-D08-13_CONTAMIN_input_atmos
ANSDK-D08-14_CONTAMIN_INPUT_point_sources
ANSDK-D08-17_CONTAMINAN_water
ANSDK-D08-18_CONTAMINAN_sediment
ANSDK-D08-19_CONTAMINAN_species
Reference sub-programme Sub-programme name
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - population characteristics
Mobile species - population characteristics
Mobile species - state of habitats
Mobile species - state of habitats
Benthic species - abundance and/or biomass
Seabed habitats - distribution and extent
Seabed habitats - distribution and extent
Seabed habitats - community characteristics
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Physical disturbance - from bottom trawling
Physical disturbance - from sand and gravel extraction
Activities extracting non-living resources (sand, gravel, dredging)
Mobile species - health status
Mobile species - health status
Mobile species - health status
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 inputs - land-based sources
Contaminant levels - in water/sediment
Contaminant levels - in water/sediment
Contaminant levels - in species, including seafood
Q4g - Sub-programmes Sub-programme ID
ANSDK-D01-03_abundance_mammals_seals
ANSDK-D01-04_abundance_mammals_porpoise
ANSDK-D01-10_population_mammals_seals
ANSDK-D01-11_population_mammals_porpoise
ANSDK-D01-17_habitats_mammals_seals
ANSDK-D01-18_habitats_mammals_porpoise
ANSDK-D01-21_habitat_demersal_sandeel
ANSDK-D01-22_seabed_distribution
ANSDK-D06-01_seabed_community
ANSDK-D06-03_abundance_softbottomflora
ANSDK-D06-04_abundance_softbottomfauna
ANSDK-D06-06_physidisturb_trawl
ANSDK-D06-07_physidisturb_dredging
ANSDK-D07-02_ACTIVITY_nonlivingresource
ANSDK-D08-01_health_birds_breeding
ANSDK-D08-02_health_fish_demersal
ANSDK-D08-03_health_fish_commercial
ANSDK-D08-04_health_fish_sandeel
ANSDK-D08-06_health_fish_coastal
ANSDK-D08-07_health_fish_migratory
ANSDK-D08-08_health_fish_migratory_pelagic
ANSDK-D08-09_mortality_birds
ANSDK-D08-10_health_hardbottomfauna
ANSDK-D08-12_health_softbottomfauna
ANSDK-D08-13_CONTAMIN_input_atmos
ANSDK-D08-14_CONTAMIN_INPUT_point_sources
ANSDK-D08-17_CONTAMINAN_water
ANSDK-D08-18_CONTAMINAN_sediment
ANSDK-D08-19_CONTAMINAN_species
Q4g - Sub-programmes Sub-programme name
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - population characteristics
Mobile species - population characteristics
Mobile species - state of habitats
Mobile species - state of habitats
Benthic species - abundance and/or biomass
Seabed habitats - distribution and extent
Seabed habitats - distribution and extent
Seabed habitats - community characteristics
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Physical disturbance - from bottom trawling
Physical disturbance - from sand and gravel extraction
Activities extracting non-living resources (sand, gravel, dredging)
Mobile species - health status
Mobile species - health status
Mobile species - health status
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 inputs - land-based sources
Contaminant levels - in water/sediment
Contaminant levels - in water/sediment
Contaminant levels - in species, including seafood
Q4k - Monitoring purpose
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact Pressurse
StateImpact
StateImpact
Activities
Activities
Activities
StateImpact
StateImpact
Activities
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
Pressurse
StateImpact Pressurse
Pressurse Measures
Pressurse
StateImpact Pressurse
Pressurse Measures
Pressurse Measures
Q4l - Links of monitoring programmes of other Directives and Conventions
Monitoring of seals is conducted in relation to the habitatsdirective in a number of Natura2000 areas including aerial surveys of haulouts during peak moulting seasn in August. The programme is included in the National Monitoring Programme for Water and Nature.
Surveys in the marine seaterritory is performed in conjunction with EU-projects (SCANS) outside the NAtional Monitoring Programme for Water and Nature as the population of harbour porpoises is shared with neighbouring countries.
Monitoring of seals is conducted in relation to the habitatsdirective in a number of Natura2000 areas including aerial surveys of haulouts during peak moulting seasn in August. The programme is included in the National Monitoring Programme for Water and Nature.
Surveys in the marine seaterritory is performed in conjunction with EU-projects (SCANS) outside the NAtional Monitoring Programme for Water and Nature as the population of harbour porpoises is shared with neighbouring countries.
Programme for species and habitats is part of the National Monitoring Programme for Water and Nature. http://naturstyrelsen.dk/media/nst/Attachments/NOVANA_del1endelig1.pdf
Monitoring under the NATURA 2000 directives contributes to the MSFD programme.
The purpose of the sand eel dredge survey is to collect sand eels buried in the seabed and compare catches (number and age composition) with the previous year's collections to assess year class strength of the lesser sand eel (Ammodytes marinus) in the different areas adopted by ICES in 2009. Data from the dredge survey is the basis for calculating a 0-group index, which is used in stock assessment. The 2014 survey is planned to be conducted with the commercial fishing vessel Salling. All species are specified and counted and weighted and station information with depth and temperature is recorded. On all new positions a bottom sample (a Van Veen grab) is taken to determine the sediment chracteristics and/or type. - 15 days at sea - 165 dredge hauls and 40 sediment grab sample distributed over 55 planned sample positions.
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
The monitoring program is developped for both the Water Frame directive and addapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It will therefor contribute to the monitoring of meassures regarding biodiversity and development for macroalgae on reefs.
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 Convention for the Protection of the marine Environment of the North-East Atlantic. http://www.ospar.org/content/content.asp?menu=01481200000000_000000_000000
Not relevant
http://www.vildtsundhed.dk/english/Activities/Surveillance
The surveys aim is to provide ICES assessment and science groups with consistent and standardized data for examining spatial and temporal changes in (a) the distribution and relative abundance of fish and fish assemblages; and (b) of the biological parameters of commercial fish species for stock assessment purposes. In terms of groundfish surveys coordinated by IBTS, the main objectives are to: 1 ) To determine the distribution and relative abundance of pre‐recruits of the main commercial species with a view of deriving recruitment indices; 2 ) To monitor changes in the stocks of commercial fish species independently of commercial fisheries data; 3 ) To monitor the distribution and relative abundance of all fish species and selected invertebrates; 4 ) To collect data for the determination of biological parameters for selected species; 5 ) To collect hydrographical and environmental information; 6 ) To determine the abundance and distribution of late herring larvae (February North Sea survey). http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20%28SISP%29/SISP1-IBTSVIII.pdf. The survey is part of the DCF - obligation 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.
The purpose of the sand eel dredge survey is to collect sand eels buried in the seabed and compare catches (number and age composition) with the previous year's collections to assess year class strength of the lesser sand eel (Ammodytes marinus) in the different areas adopted by ICES in 2009. Data from the dredge survey is the basis for calculating a 0-group index, which is used in stock assessment. The 2014 survey is planned to be conducted with the commercial fishing vessel Salling. All species are speified and counted and weighted and station information with depth and temperature is recorded. On all new positions a bottom sample (a Van Veen grab) is taken to determinied the sediment type. - 15 days at sea - 165 dredge hauls and 40 sediment grab sample distributed over 55 planned sample positions . The 2013 survey program is attached.
NOVANA OSPAR CEMP HELCOM COMBINE
ICES Working Group of International Pelagic surveys (WGIPS) has conducted a guide to the methodologies adhered to during the planning, execution and analysis phases of WGIPS coordinated surveys. The manual is not yet avalible in an online version but will be attached as an appendix. The survey coordination and documentation is done in this ICES working group and the details can be found in the ICES repport: http://www.ices.dk/sites/pub/Publication%20Reports/Expert%20Group%20Report/SSGESST/2014/WGIPS14.pdf. The survey aims to provide an annual estimate of the distribution, abundance and population structure to inform the assessment of the following herring and sprat stocks: Western Baltic Spring Spawning herring (in IV and IIIa), North Sea Autumn Spawning herring (in IV and IIIa), West of Scotland herring (in VIaN), Malin Shelf herring (in VIaN-S and VIIb,c), North Sea sprat (in IV) and Sprat in IIIa. The derived estimates and age structure of herring and sprat are used as tuning indices in the respective assessments and are submitted annually to the HAWG. The Danish contribution to the survey is in Skagerrak and Kattegat.
ICES Working Group of International Pelagic surveys (WGIPS) has conducted a guide to the methodologies adhered to during the planning, execution and analysis phases of WGIPS coordinated surveys. The manual is not yet avalible in an online version but will be attached as an appendix. The survey coordination and documentation is done in this ICES working group and the details can be found in the ICES report: http://www.ices.dk/sites/pub/Publication%20Reports/Expert%20Group%20Report/SSGESST/2014/WGIPS14.pdf. The survey objectives are listed below: • Carry out a pre-determined survey cruise track • Determine an age stratified estimate of relative abundance of herring within the survey area • Determine an age stratified estimate of relative abundance of blue whiting within the survey area • Collect biological samples from directed trawling on insonified fish echotraces to determine age structure and maturity state of the herring stock • Collect physical oceanography data from vertical profiles (CTD). • Plankton sampling (WP2 and Dyedi) A survey manual is included as an appendix MANUAL FOR INTERNATIONAL PELAGIC SURVEYS (IPS) page 7-12
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/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, 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, Randers Fjord.
NOVANA OSPAR CEMP HELCOM COMBINE
NOVANA OSPAR CEMP HELCOM COMBINE
Q5c - Features Q5c - Habitats
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed ShallRock
  • LitSed MarineCoast
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
  • LitSed RedSalinity
Q5c - Features Q5c - Species list
  • AnnexII_IV_V_Species
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • AnnexII_IV_V_Species
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • AnnexII_IV_V_Species
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • AnnexII_IV_V_Species
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • AnnexII_IV_V_Species
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • AnnexII_IV_V_Species
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • FishDemersal
  • MammalsAll
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
  • BirdsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • MammalsAll
  • MammalsSeals
  • MammalsToothedWhales
Q5c - Features Q5c - Physical/Chemical features
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • OxygenLevels
  • TopographyBathymetry
  • CurrentVelocity
  • OxygenLevels
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
Q5c - Features Q5c - Pressures
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • PhysDam_abrasion
  • PhysLoss_Seal
  • PhysDam_abrasion
  • PhysLoss_Seal
  • PhysDam_abrasion
  • PhysLoss_Seal
  • PhysDam_abrasion
  • PhysLoss_Seal
  • PhysDam_abrasion
  • PhysLoss_Seal
  • PhysDam_abrasion
  • PhysLoss_Seal
  • PhysDam_abrasion
  • PhysLoss_Seal
  • PhysDam_abrasion
  • PhysLoss_Seal
  • Acidification
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
  • IntroHazSubstOther
Q9a - Elements
  • Trend in abundance at all localities and reproductive rates at selected localities.
  • Trend in abundance.
  • Trends in population abundance.
  • Population trend in abundance.
  • The surveillance comprises the status of the habitat types and conditions of species. This subprogramme focuses on seals.
  • Seasonal trend in density/abundance
  • The funktional group sampled is the demersal planktivore. In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specified to species or species group.
  • Sandbanks and reef distribution, type and examples of species composition within the habitats in different areas.
  • Functional groups and predominant habitats
  • Annual reporting of amounts of dredge materials dumped on Danish dumping sites.
  • Other featuresCu, Hg, Ni, Zn, Cd, As, Pb, Cr and TBT
  • Habitat types:- the predominant seabed habitat types
  • Physical and chemical features: - Topography and bathymetry of the seabed
  • All bird and mammal species
  • In the manual all relevant information on the sampling type can be found. The target species is the sand eel however, all fish/ animals are specific to species or species group counted and weighted and station information with depth, temperature and oxygen is recorded.
  • In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.
  • The funktional group sampled is the demersal planktivore. In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specified to species or species group.
  • Biological effects of contaminants: PAH-specific effects (CYP1A/EROD, PAH bile metabolites), reprodutive success in eelpout (reproductive impact, malformations).
  • Functional group; Pelagic planktivore.
  • Oiled seabirds
  • Biological effects of contaminants in benthic invertebrates: Imposex and intersex (i.e. TBT-specific effects) in marine snails, Lysosomal membrane stability (general contaminant effects) in mussels
  • Biological effects of contaminants in benthic invertebrates: Imposex and intersex (i.e. TBT-specific effects) in marine snails, Lysosomal membrane stability (general contaminant effects) in mussels
  • Heavy metals (Cr, Mn, Fe, Ni, Cu, Zn, As, Cd, Pb), pesticides(19), PAH (22)
  • Hazardous substances are measured in outlet from WWTP, separate industrial discharges, stormwater outfalls and freshwater fishfarms. Estimation of transport to/impact on marine areas is not included in the programme.
  • Watersoluble pesticides (Irgarol 1051,diurone atrazine, simazine)
  • Sediment: non-synthetic metals(Cd, Pb, Hg, Cu, Zn, Ni, As, Li, Al), PAHs (20 substances incl. Naphthalene); Synthetic: organotins (TBT, DBT, MBT, phenyletin), dioxins (17 congeners+3 dioxinlike PCBs =CB77, 126 and 169), phenols (6 substances) and phthalates (5 substances, incl. DEHP)
  • Mussels: non-synthetic metals(Cd, Pb, Hg, Cu, Zn, Ni, Cr, As, Ag), PAHs (20 substances incl. Naphthalene); Synthetic: organotins (TBT, DBT, MBT, phenyletin), dioxins (17 congeners+3 dioxinlike PCBs =CB77, 126 and 169)‌‌. Fish: metals, organotins, dioxins, PCBs (incl. 7 chlorinated pesticides), PFOS (7 substances), BDE (10 congeners), HBCDD (3 substances)
Q5a - GES criteria Relevant GES criteria
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 3.1
  • 6.1
  • 6.2
  • 7.1
  • 1.6
  • 3.1
  • 6.1
  • 7.1
  • 7.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
  • 1.3
  • 1.6
  • 6.2
  • 8.1
  • 8.2
Q5b - GES indicators Relevant GES indicators
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 1.3.1
  • 1.4.1
  • 1.5.1
  • 4.3.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 1.3.1
  • 1.4.1
  • 1.5.1
  • 4.3.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 1.3.1
  • 1.4.1
  • 1.5.1
  • 4.3.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 1.3.1
  • 1.4.1
  • 1.5.1
  • 4.3.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 1.3.1
  • 1.4.1
  • 1.5.1
  • 4.3.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 1.3.1
  • 1.4.1
  • 1.5.1
  • 4.3.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.2.1
  • 1.3.1
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 6.1.2
  • 6.2.1
  • 6.2.2
  • 7.1.1
  • 7.2.1
  • 1.5.1
  • 1.5.2
  • 5.2.2
  • 5.3.2
  • 7.1.1
  • 7.2.1
  • 7.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
  • 1.1.1
  • 1.6.1
  • 2.1.1
  • 6.2.1
  • 8.1.1
  • 8.2.1
  • 8.2.2
Q9b - Parameters monitored (state/impact) Species distribution
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-2
  • MP-9b-1-1-1
  • MP-9b-1-1-2
Q9b - Parameters monitored (state/impact) Species population size
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
Q9b - Parameters monitored (state/impact) Species population characteristics
  • MP-9b-1-3-6
  • MP-9b-1-3-6
  • MP-9b-1-3-6
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • MP-9b-1-3-2
  • MP-9b-1-3-5
  • MP-9b-1-3-8
Q9b - Parameters monitored (state/impact) Species impacts
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
  • MP-9b-1-4-4
Q9b - Parameters monitored (state/impact) Habitat distribution
  • MP-9b-1-5-1
Q9b - Parameters monitored (state/impact) Habitat extent
  • MP-9b-1-6-1
Q9b - Parameters monitored (state/impact) Habitat condition (physical-chemical)
  • MP-9b-1-7-1
  • MP-9b-1-7-11
  • MP-9b-1-7-1
  • MP-9b-1-7-11
  • MP-9b-1-7-2
  • MP-9b-1-7-6
  • MP-9b-1-7-11
  • MP-9b-1-7-1
  • MP-9b-1-7-11
  • MP-9b-1-7-1
  • MP-9b-1-7-2
  • MP-9b-1-7-1
  • MP-9b-1-7-2
Q9b - Parameters monitored (state/impact) Habitat condition (biological)
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-1
  • MP-9b-1-8-2
  • MP-9b-1-8-1
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-2
  • MP-9b-1-8-3
Q9b - Parameters monitored (state/impact) Habitat impacts
  • MP-9b-1-9-2
Q9b - Parameters monitored (pressures) Pressure input
  • MP-9b-2-1-3
  • MP-9b-2-1-1
  • MP-9b-2-1-2
Q9b - Parameters monitored (pressures) Pressure output
  • MP-9b-2-2-1
  • MP-9b-2-2-1
  • MP-9b-2-2-2
  • MP-9b-2-2-7
  • MP-9b-2-2-2
  • MP-9b-2-2-2
  • MP-9b-2-2-3
  • MP-9b-2-2-4
  • MP-9b-2-2-2
  • MP-9b-2-2-3
  • MP-9b-2-2-1
  • MP-9b-2-2-4
  • MP-9b-2-2-2
Q9b - Parameters monitored (activity) Activity
  • MP-9b-3-1-2
  • MP-9b-3-1-1
  • MP-9b-3-1-2
  • MP-9b-3-1-4
  • MP-9b-3-1-1
  • MP-9b-3-1-4
Q9b Parameters monitored (other) Other
  • MP-9b-4-1-1
  • MP-9b-4-1-1
  • MP-9b-4-1-1
  • MP-9b-4-1-1
  • MP-9b-4-1-1
  • MP-9b-4-1-1
  • MP-9b-4-1-1
Q41 Spatial scope
MSland_FW
WFD_CW TerritorialWaters EEZ
MSland_FW
WFD_TW WFD_CW TerritorialWaters
MSland_FW
WFD_CW TerritorialWaters
EEZ BeyondMSwaters
WFD_TW WFD_CW TerritorialWaters EEZ
WFD_TW WFD_CW TerritorialWaters EEZ CS
WFD_CW
WFD_CW TerritorialWaters EEZ BeyondMSwaters
EEZ BeyondMSwaters
WFD_CW
TerritorialWaters
MSland_FW WFD_TW WFD_CW TerritorialWaters
EEZ BeyondMSwaters
WFD_CW EEZ BeyondMSwaters
EEZ BeyondMSwaters
WFD_CW
EEZ BeyondMSwaters
BeyondMSwaters
MSland_FW WFD_CW
WFD_CW TerritorialWaters EEZ
WFD_CW TerritorialWaters EEZ
MSland_FW WFD_TW WFD_CW TerritorialWaters
MSland_FW
WFD_TW WFD_CW
WFD_CW TerritorialWaters EEZ
WFD_CW TerritorialWaters
Q4j - Description of spatial scope
Harbour seals monitored since 1979. Grey seals monitored since 2011. All sites where seals go on land are included in the program.
Harbour porpoises occur in all Danish waters. Every 11th year an international survey (SCANS) conduct an abundace a survey covering all regional waters except for the Limfjorden.
In Danish waters there is 4 populations of harbour seals and 2 populations of grey seals. In this region the Wadden Sea harbour seal population is shared with Germany and the Netherlands and the Limfjorden population is exclusively Danish. The North Sea grey seal population is shared with the North Sea range states.
Denmark share 3 harbour porpoise poulations with teh North Sea rnage states (North Sea population), Sweden and Germany (Belt Sea population) and the Baltic proper range states (Baltic population). The North Sea poulation and half of the Belt Sea population is living within the ANSDK 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 sand-eel survey is conducted on sandbanks in the North Sea where sandeel is or has been present historically. The stations have been selected in cooperation with the industry and are fixed stations. If new stations are added to the survey sediment sample is taken to confirm that the bottom environment is suitable for sand eels.
The monitoring is not systematic. Larger scale distribution mapping of reefs, bubbling reefs and sandbanks started in 2006. (Mapping of 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.
Some areas have older monitoring than others. Monitoring started in 1989 and was expanded in 2004 to include all open water reefs designated as SAC and macroflora along coastal hard substrates The monitoring was originally intended to describe the state of the reef in relation to the Water frame directive. It now also supplies data for the state of the reefs for the habitat directive. As such most monitoring stations are found within the Natura 2000 areas
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/
Vessel monitoring systems (VMS) are used in commercial fishing to allow environmental and fisheries regulatory organizations to monitor, minimally, the position, time at a position, and course and speed of fishing vessels. They are a key part of the Danish monitoring control and surveillance programs.
All our dumping cites for dredged materials are placed within the coastal water zone.
The geographic scope of the programme depends on the needs for marin sand and gravel material.
The National Monitorin Progrmme for Water and Nature is aiming at documenting impacts of the current measures, as well as establishing a basis for future managerial decision-making.
IBTS is an international ICES coordinated survey, were Denmark gets appointed stations in Danish EZ zone as well as in international water in the North Sea. 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 40 fishing stations and 80 plankton stations in the 1st quarter survey and 50 fishing stations and 0 plankton stations in the 3rd 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 (IBTSWG) coordinating the survey. http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20%28SISP%29/SISP1-IBTSVIII.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.
The sand-eel survey is conducted on sandbanks in the North Sea where sand eel is or has been present historically. The stations have been selected in cooperation with the industry and are fixed stations. If new stations are added to the survey sediment sample is taken to confirm that the bottom environment is suitable for sand eels.
In representative coastal areas, coordinated with the monitoring activities on contaminnant levels in fish.
The purpose is to provide acoustic abundance estimates of herring and sprat in the North Sea (eastern part), Skagerrak and Kattegat.
This survey is carried out in order to investigate abundance, distribution and migrations of the Atlanto-Scandian herring, blue whiting and other pelagic fish in the Norweigian Sea and adjacent waters . Furthermore, hydrographical conditions and plankton abundance are monitored. The survey was coordinated with Norway as an international survey with participation of Norway, Iceland, Faroe Islands and EU, where the Danish R/V Dana conducted the EU survey part. The survey is carried out as a joint EU survey with participation of UK, Ireland, Netherlands, Germany, Sweden and Denmark.
All costal areas
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/ Stations in open waters located in relation to international shipping lanes. In coastal waters stations are located in representative areas, e.g. coordinated with program on contaminant-levels
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/ Stations in open waters located in relation to international shipping lanes. Stations in coastal waters staions are located in representative areas, e.g. coordinated with program on contaminant-levels
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 in this context only Kattegat - thus not Skagerrak and the North Sea). For organic cantaminants only measurents of wet deposition a two 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.
Danish part of OSPAR convention.
Danish part of OSPAR convention. Mussel stations mainly coastal, fish stations more open stations in the North Sea.
Marine Unit IDs
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
  • ANS_DK_SR_001
Q4h - Temporal scope Start date- End date
1979-9999
2011-9999
1979-9999
2011-9999
1979-9999
2011-9999
-
2004-9999
2006-9999
1989-9999
1987-9999
1990-9999
2005-9999
1986-9999
1997-9999
1932-9999
1991-9999
1995-9999
2004-9999
2004-9999
2006-9999
2004-9999
1991-9999
1998-9999
1998-9999
1989-9999
1998-9999
2001-2003
1998-9999
1998-9999
Q9h - Temporal resolution of sampling
  • Yearly
  • 6yearly
  • Yearly
  • 6yearly
  • Yearly
  • Yearly
  • Yearly
  • Oneoff
  • 6yearly
  • Continually
  • Yearly
  • Asneeded
  • Other
  • 6monthly
  • Continually
  • Yearly
  • Yearly
  • Yearly
  • Yearly
  • Continually
  • 2yearly
  • 2yearly
  • Continually
  • Yearly
  • Yearly
  • 6yearly
  • Yearly
Q9c - Monitoring method
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 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
In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specified to species or species group counted and weighted and station information with depth and temperature is recorded. On all new positions a bottom sample (a Van Veen grab) is taken to determinied the sediment type.
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
Technical program description is currently under revision. Overall method is similar but varies between three selection methods: Data is gathered by a diver either along a transect coastally or at three or four stations at different depths on open sea reefs. Previous technical standards can be seen in the folowing link: http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del4/TA04_4_1_Bloedbundsfauna.pdf http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del4/TA04_4_2_Haardbundsfauna.pdf http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del4/TA04_4_3_filtratorer.pdf http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del3/TA04_3_1_Bundvegetation.pdf
http://icesjms.oxfordjournals.org/content/68/1/245.abstract
https://www.retsinformation.dk/Forms/R0710.aspx?id=121680
The methods are described in the Danish Statutory Order No. 1169 of 3 October 2013
Passive disease surveillance in collaboration between The Danish Nature Agency and The National Veterinary Institute.
ICES methods.
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.
In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specified to species or species group counted and weighted and station information with depth and temperature is recorded. On all new positions a bottom sample (a Van Veen grab) is taken to determinied the sediment type.
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
ICES methods - following the international coordinated manual "MANUAL FOR INTERNATIONAL PELAGIC SURVEYS (IPS) " Other parameter measured in connection to health is condition in the pelagic 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. At sea the herrings aged are also analysed for fungus.
ICES methods - following the international coordinated manual "MANUAL FOR INTERNATIONAL PELAGIC SURVEYS (IPS) " Biological sampling is carried out with large og midsized pelagic midwater trawls (countrydependent), with a vertical opening of 25-35 m. Trawl metrics are monitored using a net sonde. All components of the catch from the trawl hauls is sorted and weighed; fish and other taxa are identified to species level. Fish samples are divided into species composition by weight. Length frequency and length weight data is collected for each component of the catch. Length measurements of herring, and blue whiting to be taken to the nearest 0.5cm below. Biological sampling is used to verify the composition of echotraces during echo integration. Decisions to fish on particular echotraces are largely subjective and an attempt should be made to target echotraces low density scattering layers not just high density shoals. No bottom trawl gear is used during this survey. Other parameter measured in connection to health is condition in the pelagic species. This is monitored over time to detect changes in health/ growth. Furthermore, all herring aged are also analysed for the parasite nematode Anasaki in the laboratory.
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 for 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
OSPAR Aggrement 2002-16, JAMP Guidelines for Monitoring Contaminants in Sediments (rev. 2011). www.ospar.org in “Program and measures” under “aggrements”, incoorporated into technical annexes for the national NOVANA program http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M24_Miljoefarlige_stoffer_i_sediment_ver1.pdf
OSPAR Aggrement 2002-16, JAMP Guidelines for Monitoring Contaminants in Sediments (rev. 2011). www.ospar.org in “Program and measures” under “aggrements”, incoorporated into technical annexes for the national NOVANA program http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M25_Miljoefarlige_stoffer_i_fisk.pdf http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M26_Biologisk_effektmonitering_i_fisk__ver_1_.pdf http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M28_Biologisk_effektmonitering_i_muslinger__VERSION_2_.pdf
Q9d - Description of alteration to method
The bottom sample is used to document the sediment type on the sand ell banks. The size of the grain is used to determine if the sediment is suitable for sand eel.
Not relevant.
Other parameter measured in connection to health is condition in the demersal species. This is monitored over time to detect changes in health. Furthermore, all herring aged are also analysed for the parasite nematode Anasaki in the laboratory.
Other parameter measured in connection to health is condition in the demersal species. This is monitored over time to detect changes in health. No chemicals or pollutant concentration is meassured.
Acoustic data are collected using a Simrad EK60 scientific echosounder. Split-beam transducers are mounted on the various vessels in different configurations. Several operating frequencies are used during the surveys (e.g. 18, 38, 120 and 200 kHz) for trace recognition purposes, but with 38 kHz data used to generate the abundance estimate All frequencies are to be calibrated prior to the survey. Details to be found in the manual.
Q9e - Quality assurance
  • Other
  • see link included above
  • Other
  • see link included above
  • Other
  • see link included above
  • Other
  • see link included above
  • Other
  • see link included above Technical Guide M16 Artsovervågning af sæler
  • Other
  • see link included above
  • Other
  • see input in Q4l
  • COMBINE
  • Other
  • see links included above
  • National
  • see link included above
  • Unknown
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • BEQUALM
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • Unknown
  • QUASIMEM
  • QUASIMEM
  • Other
  • COMBINE
  • QUASIMEM
  • QUASIMEM
  • QUASIMEM
  • QUASIMEM
Q9f - Quality control
OtherQC
OtherQC
OtherQC
OtherQC
OtherQC
OtherQC
RealandDelayedValidation
RealandDelayedValidation
OtherQC
DelayedValidation
DelayedValidation
DelayedValidation
Unknown
RealandDelayedValidation
RealandDelayedValidation
RealandDelayedValidation
DelayedValidation
RealandDelayedValidation
RealandDelayedValidation
Unknown
DelayedValidation
DelayedValidation
OtherQC
DelayedValidation
DelayedValidation
DelayedValidation
DelayedValidation
Q9g - Spatial resolution of sampling Q9g - Proportion of area covered %
100
90
100
90
100
10
90
100
100
100
0.67
50
2.5
100
90
90
20
100
10
75
75
Q9g - Spatial resolution of sampling Q9g - No. of samples
For the whole area it is 1/11 years.
For the North Sea population it is 1/11 years. For the Belt Sea population it is 1/5-6 years.
For the Natura2000 areas it is 1/year
Sidescan data is gatherered covering most of the bottom of the mapped Natura 2000 sites. Number of videosamles vary
In one year: 1) 32 annual open ocean reef samples are taken, 2) app 7 open ocean samples (with a total of app. 40 samples within 6 years) 3) app 50 coastal macroalgae transects are gathered every year.
34% of the total vessels operating in this area were above 12 meters in 2013
The number of samples is different every year, depending on the need for sand and gravel.
Not determined - passive sampling
around 150 trips are conducted on an annual basis and this corrispond to 325 days at sea. Indicating that 1 trip equals to 0.67% From minimum 1 station per day we sample all species with length and weight and only selected speces for age
9
As described above
10
20
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: 7 stations indirect outlet: 4 stations
3
20
25+4 (mussels+fish)
Q9i - Description of sample representivity
Monitoring frequency varies from every year to every six years for different sampling areas and sampling types within this subprogram.
The Danish marine dumping sites occupy 68km3 of our coastal waters and as all dumping events are reported with respect to total amounts of dredged material dumped. It is within this logic concluded that 100% of the 68Km is monitored. No samples are expected to be taken from the sea bottom within the proportion given above. Ass explained in C9 the data consists of material volumes and there levels of contamination with certain pollutants mentioned in 9a. These data are collected before the dredged material is dumped on the dumping sites.
The volume of extraction is monitored every quarter or more often. The volume of extraction in common areas can be seen at the Danish Nature Agency homepage: http://naturstyrelsen.dk/vandmiljoe/havet/raastoffer/statistik-om-raastoffer/ Surveys (topography, bathymetri and seabed habitat types etc.) must be carried out before licens for sand and gravel extraction can be obtained in new areas. In 2014 approx 10 new areas have been investigated. The Danish Nature Agency has since 2010 conducted surveys of a number of larger areas, e.g. the North Sea, Kattegat .
In first quarter survey we sample 40 fishing stations and 80 plankton stations and 50 fishing stations and 0 plankton stations in the 3rd quarter survey. From each station we sample all species with length and weight and only selected speces (see appendix 1a) for age and maturity
In 2014, 19 fishing days are planned
The survey is conducted as a acustic survey and trawl samples are only taken when it can be detected on the acustic. The survey has planned to conduct 40 fishing stations and 20 planktonic stations each year. This indicates that 1 fishing station will have the influence of 2.5%. The fish sample obtained from the trawl catch is divided into species by weight and by number. Length measurements are taken to the nearest 0.5 cm below for sprat and herring (and to the whole cm below for other species). For herring and sprat either representative or length stratified samples are taken for maturity, age (otolith extraction) and weight. The biological sampling includes measures to allow discrimination amongst different stocks of herring. In the Danish part of the survey the total herring estimate is divided into North Sea Autumn Spawners and Western Baltic Spring Spawners. The mean weights and mean lengths used are the same for the two stocks as they are not divided on an individual basis. The split is based on vertebral counts in the Norwegian part and on otolith shape analysis in the Danish survey area.
The survey is conducted as an acustic survey and trawl samples are only taken when it can be detected on the acustic. The survey has planned to conduct 10 fishing stations and 35 planktonic stations each year. This indicates that 1 fishing station will have the influence of 10% and a plankton station will influence around 3% of the total stations carried out by Denmark. Catches from trawl hauls are sorted and weighed; fish are identified to species level, when possible, and other taxa to higher taxonomic levels. Normally a subsample of 30–100 herring and blue whiting are sexed, aged, and measured for length and weight, and their maturity status is estimated using established methods. An additional sample of 70–300 fish is measured for length.
The estimated depositions cover the Dansih land areas and the Inner Danish Waters. Two measurement stations for heavy metals are linked to the North Sea. One measuremtent station situated about 20 km from the west coast of Jutland and one is situated on the small island Anholt in Kattegat. Measurements of wet depostions of organic contaminants are carried out at Roskilde and Sepstrup Sande in mid Jutland
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.
Fish stations are timetrend, 4 mussel stations timetrend stations (revisited yearly). Other mussel stations are placed every year to extend spatial coverage and support for MPAs or areas in risk of higher pressures
Q10a - Scale for aggregation of data
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Unknown
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
Q10b - Other scale for aggregation of data
The abundance of harbour seals should be aggregated in the four management units living in Denmark. For this region the Waddensea (part of the Netherland, German, Danish) population, Limfjorden and Kattegat (partly covering region BALDK and shared with Sweden). For grey seals the agrregation is all of the North Sea.
Porpoise abundance should be aggregated on population level to avoid movement between areas. For this region there is a North Sea and a Belt Sea population (expanding over both the ANSDK and BALDK)
The population monitoring of harbour seals should be aggregated in the four management units living in Denmark. For this region the Waddensea (part of the Netherland, German, Danish) population, Limfjorden and Kattegat (partly covering region BALDK and shared with Sweden). For grey seals the agrregation is all of the North Sea.
Porpoise abundance should be aggregated on population level to avoid movement between areas. For this region there is a North Sea 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 upon 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
http://naturstyrelsen.dk/vandmiljoe/havet/raastoffer/statistik-om-raastoffer/
n/a
Q10c - Access to monitoring data Q10c - Data type
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData Simulated
ProcessedData
ProcessedData
ProcessedData
ProcessedData
UnprocessedData ProcessedData DataProducts Simulated
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData
Simulated
Simulated
UnprocessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
ProcessedData
ProcessedData
UnprocessedData ProcessedData
ProcessedData DataProducts
ProcessedData DataProducts
Q10c - Access to monitoring data Q10c - Data access mechanism
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
URLdownload
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationInternationalDC
URLdownload
LocationNationalDC
LocationInternationalDC
LocationInternationalDC
LocationInternationalDC
LocationNationalDC
LocationNationalDC
LocationInternationalDC
LocationInternationalDC
URLview
LocationNationalDC
LocationNationalDC
LocationInternationalDC
LocationNationalDC
LocationNationalDC
LocationInternationalDC
LocationInternationalDC
Q10c - Access to monitoring data Q10c - Data access rights
Open
Open
Open
Open
Open
Open
RestrictedSpecific
Open
Open
Open
Open
RestrictedSpecific
Open
Open
Open
Open
RestrictedSpecific
RestrictedSpecific
Open
RestrictedSpecific
RestrictedSpecific
Open
Open
Open
Open
Open
Open
Open
Open
Q10c - Access to monitoring data Q10c - INSPIRE standard
HabitatsBiotopes SpeciesDistribution
SeaRegions SpeciesDistribution
HabitatsBiotopes SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
HabitatsBiotopes SeaRegions SpeciesDistribution
HabitatsBiotopes SeaRegions SpeciesDistribution
OceanographicFeatures SpeciesDistribution
HabitatsBiotopes
HabitatsBiotopes OceanographicFeatures SpeciesDistribution
HabitatsBiotopes OceanographicFeatures SpeciesDistribution
HabitatsBiotopes SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
OceanographicFeatures
Geology SeaRegions
SeaRegions SpeciesDistribution
OceanographicFeatures SpeciesDistribution
OceanographicFeatures SpeciesDistribution
HabitatsBiotopes SpeciesDistribution
OceanographicFeatures
OceanographicFeatures SpeciesDistribution
HabitatsBiotopes OceanographicFeatures SpeciesDistribution
SeaRegions SpeciesDistribution
OceanographicFeatures SeaRegions
HabitatsBiotopes OceanographicFeatures SeaRegions SpeciesDistribution
OceanographicFeatures SeaRegions
SeaRegions
OceanographicFeatures SeaRegions
OceanographicFeatures SeaRegions
OceanographicFeatures SeaRegions
Q10c - Access to monitoring data Q10c Date data are available
2014-11
2014-11
2014-11
2014-11
2014-11
2014-11
2015-02
2015-12
2015-12
2015-04
2015-04
2014-10
2014-12
2014-09
2015-12
2015-04
2015-04
2015-02
2015-12
2015-03
2015-03
2015-12
2015-04
2015-04
1990-01
2015-12
2014-12
1999-01
1999-01
Q10c - Access to monitoring data Q10c - Data update frequency
Yearly
6yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Oneoff
Yearly
Yearly
2yearly
3monthly
Yearly
Asneeded
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Asneeded
2yearly
2yearly
Yearly
Yearly
2yearly
Yearly
Yearly
Q10d - Description of data access
Data are published in the yearly reportings under the National Monitoring Programme for Water and Nature, and will be included also in the forthcoming MSFD Article 8 initial assessmernt due in 2018.
Data will be reported in yearly publications under the NAtional Monitoring Programme for Water and Nature as well as in the forthcoming MSFD Article 8 initial assessment due in 2018.
The data will be reported yearly under the National Monitoring Programme for Water and Nature as well as in the forthcoming MSFD art. 8 initial assessment due in 2018.
Data will be reported in the yearly reports under the National Monitoring Programme for Water and Nature as well as in the forthcoming MSFD art 8 initial assessment due in 2018
Data are reported on a yearly basis under the National Monitoring Programme for Water and Nature 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 and in the forthcoming MSFD art 8 intial assessment due in 2018.
Sediment charactersitics will be determined and included in the forthcoming MSFD Articel 8 intiatial 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/
Reports and baseline analysis for instance http://dce2.au.dk/pub/SR77.pdf pp 69-89, as well as in the fothcoming MSFD art. 8 initial assessment due in 2018.
http://www.miljoeportal.dk/Sider/Forside.aspx
http://www.miljoeportal.dk/Sider/Forside.aspx
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.
The information will be made available in an annual report on dumping activities on OSPARS homepage
Data are available from http://www.geus.dk/DK/about-geus/departments/geol-data-centre/Sider/wellarc-dk.aspx and http://naturstyrelsen.dk/vandmiljoe/havet/raastoffer/statistik-om-raastoffer/
Data will be reported in yearly report under the National Monitoring Programme for Water and Nature as well as in the fortcomin MSFD artciel 8 intial assessment due in 2018
In ICES DATRAS database.
In ICES Regional data base (RDB).
Data will be available for managerial purposes of sandeels management at national data center at DTU Aqua, but will also be made available in the forthcoming MSFD art. 8 initial assessment due in 2018.
Data are reported in yearly reports under the National Monitoring Programme for Water and Nature as well as in the forthcomin MSFD art 8 initial assessment due in 2018
ICES is presently working on constructing a database where all aquatic data can be uploaded and stored. Presently DTU Aqua is hosting this database.
ICES is presently working on constructing a database where all aquatic data can be uploaded and stored. Presently DTU Aqua is hosting this database.
n/a
Yearly National report under the National Monitoring Programme for Water and Nature, NOVANA, and in the forthcoming MSFD art 8 initial assessment in 2018
Yearly National report. under the National Monitoring Programme for Water and Nature as well as in the forthcoming MSFD art 8 initial assessement due in 2018
Data are published yearly under the National Monitopring Prgroamme for Water and Nature, as well as in the forthcoming MSFD art 8 initial assessment due in 2018.
Data are published in yearly reports under the NAtional Monitoring Programme for Water and Nature, as well as in the forthcoming MSFD art 8 initial assessment due in 2018
Data and information will be available in yearly reportings under the National Monitoring Programme for Water and Nature, and in the forthcoming article 8 assessment in 2018.
data is published in yearly reports under the NAtional Monitoring Programme for Water and NAture, 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 Progrqmme for Water and NAture, NOVANA and in the forthcoming MSFD art 8 initial assessment in 2018.