Member State report / Art11 / 2014 / D4 / 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 D4 Food webs/D1 Ecosystems
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_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
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_WaterColumnHabitats
MP_D1_4_6_WaterColumnHabitats
MP_D3
MP_D3
MP_D3
MP_D3
MP_D3
MP_D3
MP_D5
MP_D5
MP_D5
MP_D5
MP_D5
MP_D5
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-FISH-D01-D04
ANSDK-FISH-D01-D04
ANSDK-FISH-D01-D04
ANSDK-FISH-D01-D04
ANSDK-FISH-D01-D04
ANSDK-FISH-D01-D04
ANSDK-FISH-D01-D04
ANSDK-FISH-D01-D04
ANSDK-FISH-D01-D04
ANSDK-FISH-D01-D04
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
ANSDK-D01
ANSDK-D03
ANSDK-D03
ANSDK-D03
ANSDK-D03
ANSDK-D03
ANSDK-D03
ANSDK-D05
ANSDK-D05
ANSDK-D05
ANSDK-D05
ANSDK-D05
ANSDK-D05
Q4f - Programme description
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
The programme centers around providing data for the calculation of abundance, population charactersitics and biomasses. Furthermore integrated in the programme are also programme elements from other programmes eg. under descriptor 8. The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function. Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.
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
Monitoring of water cloumn habitats consists of the following sub-programmes: Pelagic community characteristics (phytoplankton and zooplankton species composition, abundance and/or biomass. In addition water column relevant monitoring is performed in the program packages for eutrophication and biodiversity.
Monitoring of water cloumn habitats consists of the following sub-programmes: Pelagic community characteristics (phytoplankton and zooplankton species composition, abundance and/or biomass. In addition water column relevant monitoring is performed in the program packages for eutrophication and biodiversity.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes.
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes.
The eutrophication programme sensu strictu forms the central element of the National Monitoring Programme for Water and Nature, NOVANA. Together with the eutrophication programme other programmes relate to ecosystem components contained elsewhere in the MSFD-programme. The NOVANA programme focusses on inputs of pollutants, trends, impact and status of the environment and aims at providing a basis for environmental managerial decisions.
The eutrophication programme sensu strictu forms the central element of the National Monitoring Programme for Water and Nature, NOVANA. Together with the eutrophication programme other programmes relate to ecosystem components contained elsewhere in the MSFD-programme. The NOVANA programme focusses on inputs of pollutants, trends, impact and status of the environment and aims at providing a basis for environmental managerial decisions.
The eutrophication programme sensu strictu forms the central element of the National Monitoring Programme for Water and Nature, NOVANA. Together with the eutrophication programme other programmes relate to ecosystem components contained elsewhere in the MSFD-programme. The NOVANA programme focusses on inputs of pollutants, trends, impact and status of the environment and aims at providing a basis for environmental managerial decisions.
The eutrophication programme sensu strictu forms the central element of the National Monitoring Programme for Water and Nature, NOVANA. Together with the eutrophication programme other programmes relate to ecosystem components contained elsewhere in the MSFD-programme. The NOVANA programme focusses on inputs of pollutants, trends, impact and status of the environment and aims at providing a basis for environmental managerial decisions.
The eutrophication programme sensu strictu forms the central element of the National Monitoring Programme for Water and Nature, NOVANA. Together with the eutrophication programme other programmes relate to ecosystem components contained elsewhere in the MSFD-programme. The NOVANA programme focusses on inputs of pollutants, trends, impact and status of the environment and aims at providing a basis for environmental managerial decisions.
The eutrophication programme sensu strictu forms the central element of the National Monitoring Programme for Water and Nature, NOVANA. Together with the eutrophication programme other programmes relate to ecosystem components contained elsewhere in the MSFD-programme. The NOVANA programme focusses on inputs of pollutants, trends, impact and status of the environment and aims at providing a basis for environmental managerial decisions.
Q5e - Natural variability
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • Qualitative
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  • Qualitative
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  • Quantiative
  • Quantiative
  • ExpertOpinion
  • Qualitative
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  • Qualitative
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  • Qualitative
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  • Qualitative
Q5d - Adequacy for assessment of GES Q5d - Adequate data
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
N
N
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
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate capacity
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5f - Description of programme for GES assessment
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry”. DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry”. DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry”. DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry”. DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry”. DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry”. DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).
The programme provides data on key indicators for descriptor 4. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 4. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for establishing of quantitative GES reference values.
According to coordination in ICES
According to coordination in ICES
According to coordination in ICES
According to coordination in ICES
According to coordination in ICES
According to coordination in ICES
The programme provides data on key indicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.
The programme provides data on key indicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.
Q5g - Gap-filling date for GES assessment
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2018
By2018
By2014
By2014
By2014
By2014
By2014
By2014
By2018
By2018
By2018
By2018
By2018
By2018
Q5h - Plans to implement monitoring for GES assessment
monitoring in the North Sea and Skagerrak is being phased in from 2015.
monitoring in the North Sea and Skagerrak is being phased in from 2015.
Eutrophication programme in the North Sea and Skagerrak was put in operation in August 2014.
Eutrophication programme in the North Sea and Skagerrak was put in operation in August 2014.
Eutrophication programme in the North Sea and Skagerrak was put in operation in August 2014.
Eutrophication programme in the North Sea and Skagerrak was put in operation in August 2014.
Eutrophication programme in the North Sea and Skagerrak was put in operation in August 2014.
Eutrophication programme in the North Sea and Skagerrak was put in operation in August 2014.
Q6a -Relevant targets Q6a - Environmental target
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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_18_ANS DK_21_ANS DK_32_ANS
DK_18_ANS DK_21_ANS DK_32_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
Q6a -Relevant targets Q6a - Associated indicator
DK_17_ANS
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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_18_ANS DK_21_ANS DK_32_ANS
DK_18_ANS DK_21_ANS DK_32_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
DK_18_ANS DK_19_ANS DK_22_ANS DK_23_ANS DK_24_ANS DK_25_ANS DK_32_ANS DK_33_ANS DK_34_ANS DK_35_ANS DK_49_ANS DK_52_ANS
Q6b - Adequacy for assessment of targets Q6b_SuitableData
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
N
N
N
N
N
N
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
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 earlier and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf
The programme provides data on key indicators for descriptor 4. 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 4. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.
The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.
Q6e - Gap-filling date for targets assessment
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2018
By2018
By2014
By2014
By2014
By2014
By2014
By2014
By2018
By2018
By2018
By2018
By2018
By2018
Q6f - Plans to implement monitoring for targets assessment
monitoring in the North Sea and Skagerrak is being phased in from 2015.
monitoring in the North Sea and Skagerrak is being phased in from 2015.
Monitoring in the Danish part of the North Sea and Skagerrak was started in 2014 and will be fully phased in by 2018.
Monitoring in the Danish part of the North Sea and Skagerrak was started in 2014 and will be fully phased in by 2018.
Monitoring in the Danish part of the North Sea and Skagerrak was started in 2014 and will be fully phased in by 2018.
Monitoring in the Danish part of the North Sea and Skagerrak was started in 2014 and will be fully phased in by 2018.
Monitoring in the Danish part of the North Sea and Skagerrak was started in 2014 and will be fully phased in by 2018.
Monitoring in the Danish part of the North Sea and Skagerrak was started in 2014 and will be fully phased in by 2018.
Q7a - Relevant activities
  • Fisheries
  • Fisheries
  • Fisheries
  • Fisheries
  • Fisheries
  • Fisheries
  • Fisheries
  • Fisheries
  • Fisheries
  • Fisheries
  • 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
  • AgricultForestry
  • Industry
  • Urban
  • AgricultForestry
  • Industry
  • Urban
  • Aquaculture
  • Fisheries
  • SeaweedOtherSeafood
  • Aquaculture
  • Fisheries
  • SeaweedOtherSeafood
  • Aquaculture
  • Fisheries
  • SeaweedOtherSeafood
  • Aquaculture
  • Fisheries
  • SeaweedOtherSeafood
  • Aquaculture
  • Fisheries
  • SeaweedOtherSeafood
  • Aquaculture
  • Fisheries
  • SeaweedOtherSeafood
  • AgricultForestry
  • Aquaculture
  • Industry
  • Shipping
  • Urban
  • AgricultForestry
  • Aquaculture
  • Industry
  • Shipping
  • Urban
  • AgricultForestry
  • Aquaculture
  • Industry
  • Shipping
  • Urban
  • AgricultForestry
  • Aquaculture
  • Industry
  • Shipping
  • Urban
  • AgricultForestry
  • Aquaculture
  • Industry
  • Shipping
  • Urban
  • AgricultForestry
  • Aquaculture
  • Industry
  • Shipping
  • Urban
Q7b - Description of monitoring of activities
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs.
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 provide data on key indicators in the water column together with the relevant pressures impacting the biodiversity and habitat quality of the water column.
The programme provide data on key indicators in the water column together with the relevant pressures impacting the biodiversity and habitat quality of the water column.
According to guidelines of ICES agreements
According to guidelines of ICES agreements
According to guidelines of ICES agreements
According to guidelines of ICES agreements
According to guidelines of ICES agreements
According to guidelines of ICES agreements
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM and OSPAR guidelines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM and OSPAR guidelines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM and OSPAR guidelines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM and OSPAR guidelines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM and OSPAR guidelines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.
Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM and OSPAR guidelines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.
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
Subprogrammes contained in the programme enables monitoring of the land-based inputs that will make it possible to assess the effectiveness of possible measures regulating the inputs.
Subprogrammes contained in the programme enables monitoring of the land-based inputs that will make it possible to assess the effectiveness of possible measures regulating the inputs.
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
  • HELCOM
  • OSPAR
  • CFP-DC-MAP
  • HELCOM
  • OSPAR
  • CFP-DC-MAP
  • HELCOM
  • OSPAR
  • CFP-DC-MAP
  • HELCOM
  • OSPAR
  • CFP-DC-MAP
  • HELCOM
  • OSPAR
  • CFP-DC-MAP
  • HELCOM
  • OSPAR
  • CFP-DC-MAP
  • HELCOM
  • OSPAR
  • CFP-DC-MAP
  • HELCOM
  • OSPAR
  • CFP-DC-MAP
  • HELCOM
  • OSPAR
  • CFP-DC-MAP
  • HELCOM
  • OSPAR
  • 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
  • HELCOM
  • OSPAR
  • WFD
  • HELCOM
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • CFP-DC-MAP
  • CFP-DC-MAP
  • CFP-DC-MAP
  • CFP-DC-MAP
  • CFP-DC-MAP
  • BathingWater
  • Birds
  • HELCOM
  • Habitats
  • Nitrates
  • OSPAR
  • UWWTD
  • WFD
  • BathingWater
  • Birds
  • HELCOM
  • Habitats
  • Nitrates
  • OSPAR
  • UWWTD
  • WFD
  • BathingWater
  • Birds
  • HELCOM
  • Habitats
  • Nitrates
  • OSPAR
  • UWWTD
  • WFD
  • BathingWater
  • Birds
  • HELCOM
  • Habitats
  • Nitrates
  • OSPAR
  • UWWTD
  • WFD
  • BathingWater
  • Birds
  • HELCOM
  • Habitats
  • Nitrates
  • OSPAR
  • UWWTD
  • WFD
  • BathingWater
  • Birds
  • HELCOM
  • Habitats
  • Nitrates
  • OSPAR
  • UWWTD
  • WFD
Reference sub-programme Sub-programme ID
ANSDK-D01-05_abundance_fish_coastal
ANSDK-D01-06a_abundance_fish_migratory
ANSDK-D01-06b_abund_fish_migratory_pelagic
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-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-D04-01_community_phytoplankton
ANSDK-D04-02_community_zooplankton
ANSDK-D03-04_mortal_fisheries_birds
ANSDK-D03-05_mortal_fisheries_porpoise
ANSDK-D03-06_mortal_fisheries_seals
ANSDK-D03-08_mortal_fish_coastal
ANSDK-D03-09_mortal_fish_migrat_pelagic
ANSDK-D03-10_mortal_fish_offsh_commercial
ANSDK-D05-01_micropath_water
ANSDK-D05-02_watercolumn_physical
ANSDK-D05-03_watercolumn_chemical
ANSDK-D05-04_PLANKTONBLOOM
ANSDK-D05-06_NUTRI_input_atmos
Reference sub-programme Sub-programme name
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - health status
Mobile species - health status
Mobile species - health status
Mobile species - health status
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
Pelagic habitats - community characteristics
Pelagic habitats - community characteristics
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Nutrient inputs - land-based sources
Microbial pathogen levels - in water column (bathing waters)
Water column - physical characteristics
Water column - chemical characteristics
Plankton blooms (biomass, frequency)
Nutrient inputs - from atmosphere
Q4g - Sub-programmes Sub-programme ID
ANSDK-D01-05_abundance_fish_coastal
ANSDK-D01-06a_abundance_fish_migratory
ANSDK-D01-06b_abund_fish_migratory_pelagic
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-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-D04-01_community_phytoplankton
ANSDK-D04-02_community_zooplankton
ANSDK-D03-04_mortal_fisheries_birds
ANSDK-D03-05_mortal_fisheries_porpoise
ANSDK-D03-06_mortal_fisheries_seals
ANSDK-D03-08_mortal_fish_coastal
ANSDK-D03-09_mortal_fish_migrat_pelagic
ANSDK-D03-10_mortal_fish_offsh_commercial
ANSDK-D05-01_micropath_water
ANSDK-D05-02_watercolumn_physical
ANSDK-D05-03_watercolumn_chemical
ANSDK-D05-04_PLANKTONBLOOM
ANSDK-D05-06_NUTRI_input_atmos
Q4g - Sub-programmes Sub-programme name
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - health status
Mobile species - health status
Mobile species - health status
Mobile species - health status
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
Pelagic habitats - community characteristics
Pelagic habitats - community characteristics
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Nutrient inputs - land-based sources
Microbial pathogen levels - in water column (bathing waters)
Water column - physical characteristics
Water column - chemical characteristics
Plankton blooms (biomass, frequency)
Nutrient inputs - from atmosphere
Q4k - Monitoring purpose
StateImpact
StateImpact
StateImpact
StateImpact
Activities
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
Activities
Activities
Activities
StateImpact
StateImpact
Activities
Activities
StateImpact
StateImpact
StateImpact
Pressurse Measures
Q4l - Links of monitoring programmes of other Directives and Conventions
Catches from the recreational fisheries are registered on a voluntary basis by ”key” fishermen at fixed stations in most parts of the Danish coasts. The catches are performed with standard gillnets (one mesh size, 65 mm) and/or fyke nets, with up to 3 samples monthly in the beginning of each month, and from around April to November. Because of the mesh size used, the gillnets sample mostly adults, whereas juveniles of flounder and cod may be caught in the fyke nets. At present about 100+ fishers are invovled in the project. the last report with a detailed description can be down loaded http://orbit.dtu.dk/files/100552186/Publishers_version.pdf
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 repport 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
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
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.
Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.6 shows the position of the stations. 33% of the stations are in the BALDK area and 67% of the stations are in ANSDK area. Technical manual for the marine survey http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ Describe the procedure for sampling in the field and the quality control of the datasets collected. The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR.
Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.6 shows the position of the stations. 17% of the stations are in the BALDK area and 83% 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.
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.
Catches from the recreational fisheries are registered on a voluntary basis by ”key” fishermen at fixed stations in most parts of the Danish coasts. The catches are performed with standard gillnets (one mesh size, 65 mm) and/or fyke nets, with up to 3 samples monthly in the beginning of each month, and from around April to November. Because of the mesh size used, the gillnets sample mostly adults, whereas juveniles of flounder and cod may be caught in the fyke nets. At present about 100+ fishers are invovled in the project. the last report with a detailed description can be downloaded: http://orbit.dtu.dk/files/100552186/Publishers_version.pdf
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 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.
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.
Hereby link to the EU Bathing Water Directive (Directive 2006/7/EC of 15 February 2006): http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:064:0037:0051:EN:PDF. Please find also link to the Danish Statutory order concerning the bathing water quality: (BEK no. 939 of 18/09/2012) https://www.retsinformation.dk/forms/R0710.aspx?id=143189.
Details can bee found in The national survey program (NOVANA); http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.1 shows the position of the stations. 63% of the stations are in the BALDK area and 37% of the stations are in ANSDK area. Also se figur 8.9 that show addition station sampeled primæry during the season where hypoxia cann occur. Technical manual for the marine survey http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ Describe the procedure for sampling in the field and the quality control of the datasets collected. The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR.
Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.1 shows the position of the stations. 63% of the stations are in the BALDK area and 37% of the stations are in ANSDK area. Also se figur 8.9 that show addition station sampeled primæry during the season where hypoxia cann occur. Technical manual for the marine survey http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ Describe the procedure for sampling in the field and the quality control of the datasets collected. The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR.
Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.6 shows the position of the stations. 33% of the stations are in the BALDK area and 67% of the stations are in ANSDK area. Technical manual for the marine survey: http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ Describe the procedure for sampling in the field and the quality control of the datasets collected. The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR.
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).
Q5c - Features Q5c - Habitats
  • RedSalinity MarineCoast
  • RedSalinity MarineCoast
  • LitSed WaterColumnHabitatsAll MarineCoast
  • LitSed WaterColumnHabitatsAll MarineCoast
  • LitSed WaterColumnHabitatsAll MarineCoast
  • LitSed WaterColumnHabitatsAll MarineCoast
  • LitSed WaterColumnHabitatsAll MarineCoast
  • LitSed WaterColumnHabitatsAll MarineCoast
  • LitSed
  • LitSed
  • LitSed
  • LitSed
  • LitSed
  • LitSed
Q5c - Features Q5c - Species list
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • AnnexII_IV_V_Species
  • CephalopodsAll
  • CephalopodsCoastShelf
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishDemersalElasmobranchs
  • FishPelagic
  • 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
  • MammalsAll
  • MammalsAll
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishPelagic
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishPelagic
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishPelagic
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishPelagic
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishPelagic
  • CephalopodsAll
  • FishAll
  • FishCoastal
  • FishDemersal
  • FishPelagic
  • AnnexII_IV_V_Species
  • AnnexII_IV_V_Species
  • AnnexII_IV_V_Species
  • AnnexII_IV_V_Species
  • AnnexII_IV_V_Species
  • AnnexII_IV_V_Species
Q5c - Features Q5c - Physical/Chemical features
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • TopographyBathymetry
  • Transparency
  • Turbidity
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • TopographyBathymetry
  • Transparency
  • Turbidity
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • CurrentVelocity
  • NutrientLevels
  • OxygenLevels
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • pH
  • CurrentVelocity
  • NutrientLevels
  • OxygenLevels
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • pH
  • CurrentVelocity
  • NutrientLevels
  • OxygenLevels
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • pH
  • CurrentVelocity
  • NutrientLevels
  • OxygenLevels
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • pH
  • CurrentVelocity
  • NutrientLevels
  • OxygenLevels
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • pH
  • CurrentVelocity
  • NutrientLevels
  • OxygenLevels
  • Salinity
  • SeaBottomTemperature
  • SeaSurfaceTemperature
  • Transparency
  • pH
Q5c - Features Q5c - Pressures
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • AcutePollutionEvents
  • ExtractSpeciesFishShellfish
  • Noise
  • PhysDisturbance
  • ChangeSalinity
  • ChangeThermal
  • IntroHazSubstOther
  • NutrientOrgEnrich
  • ChangeSalinity
  • ChangeThermal
  • IntroHazSubstOther
  • NutrientOrgEnrich
  • ExtractSpeciesFishShellfish
  • Litter
  • ExtractSpeciesFishShellfish
  • Litter
  • ExtractSpeciesFishShellfish
  • Litter
  • ExtractSpeciesFishShellfish
  • Litter
  • ExtractSpeciesFishShellfish
  • Litter
  • ExtractSpeciesFishShellfish
  • Litter
  • NutrientOrgEnrich
  • NutrientOrgEnrich
  • NutrientOrgEnrich
  • NutrientOrgEnrich
  • NutrientOrgEnrich
  • NutrientOrgEnrich
Q9a - Elements
  • Most frequently occurring species in the combined database are flounder (Platichtys flesus), eel (Anguilla anguilla), eel-pout (Zoarces viviparus) and cod (Gadus morhua).
  • commercial fish species and non-commercial fish species
  • Functional group; Pelagic planktivore.
  • 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).
  • 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
  • phytoplankton communities, species, biomass and primary production, chlorophyll a and fluoroscens.
  • zooplankton community composition, species, abundance and biomass
  • In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.
  • In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.
  • In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.
  • Most frequently occurring species in the combined database are flounder (Platichtys flesus), eel (Anguilla anguilla), eel-pout (Zoarces viviparus) and cod (Gadus morhua).
  • Functional group; Pelagic planktivore.
  • 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.
  • Pressures.The data to be monitored in the current program are: Intestinal enterococci and E. coli.
  • CTD, fluorescens and light attenuation
  • concentrations of nutrients in the water cloumn (nitrate,nitrite, ammonium, fosfat, silicate, total nitrogen (TN) and total fosfat(TP).
  • focus on algal blooms including nuisance blooms.
  • Eutrophying inorganic nitrogen and phosphorous
Q5a - GES criteria Relevant GES criteria
  • 4.2
  • 4.2
  • 4.2
  • 4.2
  • 4.2
  • 4.2
  • 4.2
  • 4.2
  • 4.2
  • 4.2
  • 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
  • 4.3
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 10.1
  • 10.2
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 9.1
  • 1.1
  • 1.2
  • 1.3
  • 10.1
  • 10.2
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 9.1
  • 1.1
  • 1.2
  • 1.3
  • 10.1
  • 10.2
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 9.1
  • 1.1
  • 1.2
  • 1.3
  • 10.1
  • 10.2
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 9.1
  • 1.1
  • 1.2
  • 1.3
  • 10.1
  • 10.2
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 9.1
  • 1.1
  • 1.2
  • 1.3
  • 10.1
  • 10.2
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 9.1
  • 1.1
  • 1.2
  • 4.3
  • 5.1
  • 5.2
  • 5.3
  • 1.1
  • 1.2
  • 4.3
  • 5.1
  • 5.2
  • 5.3
  • 1.1
  • 1.2
  • 4.3
  • 5.1
  • 5.2
  • 5.3
  • 1.1
  • 1.2
  • 4.3
  • 5.1
  • 5.2
  • 5.3
  • 1.1
  • 1.2
  • 4.3
  • 5.1
  • 5.2
  • 5.3
  • 1.1
  • 1.2
  • 4.3
  • 5.1
  • 5.2
  • 5.3
Q5b - GES indicators Relevant GES indicators
  • 4.2.1
  • 4.2.1
  • 4.2.1
  • 4.2.1
  • 4.2.1
  • 4.2.1
  • 4.2.1
  • 4.2.1
  • 4.2.1
  • 4.2.1
  • 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
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 1.3.1
  • 1.4.1
  • 1.5.1
  • 4.3.1
  • 4.3.1
  • 4.3.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 3.3.1
  • 4.2.1
  • 5.1.1
  • 5.2.1
  • 5.2.2
  • 5.2.3
  • 5.3.1
  • 5.3.2
  • 6.2.2
  • 5.1.1
  • 5.2.1
  • 5.2.2
  • 5.2.3
  • 5.3.1
  • 5.3.2
  • 6.2.2
  • 5.1.1
  • 5.2.1
  • 5.2.2
  • 5.2.3
  • 5.3.1
  • 5.3.2
  • 6.2.2
  • 5.1.1
  • 5.2.1
  • 5.2.2
  • 5.2.3
  • 5.3.1
  • 5.3.2
  • 6.2.2
  • 5.1.1
  • 5.2.1
  • 5.2.2
  • 5.2.3
  • 5.3.1
  • 5.3.2
  • 6.2.2
  • 5.1.1
  • 5.2.1
  • 5.2.2
  • 5.2.3
  • 5.3.1
  • 5.3.2
  • 6.2.2
Q9b - Parameters monitored (state/impact) Species distribution
  • 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
  • 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-1-1-1
  • 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-1-1-1
Q9b - Parameters monitored (state/impact) Species population size
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • 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-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
Q9b - Parameters monitored (state/impact) Species population characteristics
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • 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-1-3-6
  • 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-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
Q9b - Parameters monitored (state/impact) Species impacts
  • MP-9b-1-4-1
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-3
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-3
Q9b - Parameters monitored (state/impact) Habitat distribution
Q9b - Parameters monitored (state/impact) Habitat extent
Q9b - Parameters monitored (state/impact) Habitat condition (physical-chemical)
  • MP-9b-1-7-1
  • MP-9b-1-7-1
  • MP-9b-1-7-2
  • MP-9b-1-7-1
  • MP-9b-1-7-2
  • 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-1-7-11
  • MP-9b-1-7-11
  • MP-9b-1-7-11
  • MP-9b-1-7-1
  • MP-9b-1-7-1
  • MP-9b-1-7-2
  • MP-9b-1-7-11
  • MP-9b-1-7-1
  • MP-9b-1-7-2
  • MP-9b-1-7-6
  • MP-9b-1-7-7
Q9b - Parameters monitored (state/impact) Habitat condition (biological)
  • 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
  • MP-9b-1-8-4
  • 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
  • MP-9b-1-8-4
Q9b - Parameters monitored (state/impact) Habitat impacts
  • MP-9b-1-9-2
  • MP-9b-1-9-2
  • MP-9b-1-9-2
  • MP-9b-1-9-2
  • MP-9b-1-9-2
Q9b - Parameters monitored (pressures) Pressure input
  • MP-9b-2-1-1
Q9b - Parameters monitored (pressures) Pressure output
  • MP-9b-2-2-7
  • MP-9b-2-2-2
  • MP-9b-2-2-3
  • MP-9b-2-2-3
Q9b - Parameters monitored (activity) Activity
  • MP-9b-3-1-1
  • MP-9b-3-1-4
  • MP-9b-3-1-1
  • MP-9b-3-1-4
  • MP-9b-3-1-1
  • MP-9b-3-1-4
  • MP-9b-3-1-1
  • MP-9b-3-1-4
  • 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
Q41 Spatial scope
WFD_CW
EEZ BeyondMSwaters
BeyondMSwaters
EEZ BeyondMSwaters
WFD_CW EEZ BeyondMSwaters
EEZ BeyondMSwaters
WFD_CW
MSland_FW
WFD_CW TerritorialWaters EEZ
MSland_FW
WFD_TW WFD_CW TerritorialWaters
MSland_FW
WFD_CW TerritorialWaters
WFD_CW TerritorialWaters EEZ CS
WFD_CW TerritorialWaters EEZ BeyondMSwaters
WFD_CW EEZ BeyondMSwaters
WFD_CW EEZ BeyondMSwaters
WFD_CW EEZ BeyondMSwaters
WFD_CW
BeyondMSwaters
WFD_CW EEZ BeyondMSwaters
WFD_CW
WFD_CW TerritorialWaters EEZ BeyondMSwaters
WFD_CW TerritorialWaters EEZ BeyondMSwaters
WFD_CW TerritorialWaters EEZ CS
MSland_FW WFD_TW WFD_CW TerritorialWaters
Q4j - Description of spatial scope
the programme aims at determining the abundance and diversity of fish in coastal areas.
The purpose is to provide acoustic abundance estimates of herring and sprat in the North Sea (east-ern 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.
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.
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 program including rationale for the geographic scope can be found here: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ The aim of the National Monitoring Programe for Water and Nature is to document the impacts of the current prorammes of measures, as well as to establish a basis for future environmental management of the Daniash sea territories.
The program including rationale for the geographic scope can be found here: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ The aim of the National Monitoring Programme for Water and Nature is to document the impacts of the current programes of measures as well as to establish the basis for future environmental management of the Danish sea territories.
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter. The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system.
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter. The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system.
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter. The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system.
Project has been launched in order to ascertain the species distribution along the coastal strips of Denmark.
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.
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter. The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system.
This program includes the entire coastline, inland waters (estuaries) and lakes.
The program including rationale for the geographic scope can be found here; http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ The aim of the National Monitoring Progrmamme for Water and Nature is to document the impacts of the current programmes of measures as well as to establish the basis for future environmental management decisions.
The program including rationale for the geographic scope can be found here: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ The aim of the National Monitoring Programme for Water and Nature is to document the impacts of the current programems of measures as well as to establish the basis for future ebvironmental manaement decisions on the Danish sea territories.
The program including rationale for the geographic scope can be found here: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ The aim of the National Monitorin Prorame for Water and Nature is to document the impact of prorammes of measures as well as to establish a basis for future environmental mangement decisions in the Danish sea territory.
The Danish monitoring program for air quality and depositons is based on a few coastal fixed measurements stations in combination with modelcalculations that cover all the Danish marins waters. The quality of the model calculations is based on comparisons with the results from the monitoring stations. The aim of the National Monitoring Programme for Water and Nature is to document the impacts of the current programmes of measures, as well as to establiosh a basis for future environmental management decisions on the Danish sea territory.
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
-
-
-
2005-9999
2006-9999
2004-9999
1991-9999
1995-9999
2004-9999
2004-9999
1979-9999
2011-9999
1979-9999
2011-9999
1979-9999
2011-9999
1987-9999
1990-9999
1995-9999
1995-9999
1995-9999
2005-9999
2004-9999
1995-9999
-
1975-9999
1987-9999
1987-9999
1987-9999
1989-9999
Q9h - Temporal resolution of sampling
  • Monthly
  • Yearly
  • Yearly
  • 6monthly
  • Continually
  • Yearly
  • Yearly
  • Yearly
  • 6yearly
  • Yearly
  • 6yearly
  • Yearly
  • Yearly
  • Yearly
  • Yearly
  • Continually
  • Continually
  • Continually
  • Monthly
  • Yearly
  • Continually
  • Yearly
  • Monthly
  • Monthly
  • Monthly
  • Continually
Q9c - Monitoring method
In this project 102 voluntary recreational fishermen participated, using either gillnets, fyke-nets or both gear types. Note that the results resented in this report represent catches reported by recreational fishermen. All species have caught have been registered and length measurements have been taken. The results showed a high fish biodiversity in Danish coastal waters. A total of 49 fish species were registered in gillnets and 72 in fyke-nets. This projec represent the largest and longest time series on catches in gillnets and fyke-nets along the Danish coasts.
ICES methods - following the international coordinated manual "MANUAL FOR INTERNATIONAL PELAGIC SURVEYS (IPS)".
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.
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
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
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M07_Klorofyl_a__VERSION_2_.pdf http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M05_Fluorescens_ver1.pdf
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_6_Mikrozooplankton.pdf http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_7_Mesozooplankton.pdf
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.
In this project 102 voluntary recreational fishermen participated, using either gillnets, fyke-nets or both gear types. Note that the results resented in this report represent catches reported by recreational fishermen. All species have caught have been registered and length measurements have been taken. The results showed a high fish biodiversity in Danish coastal waters. A total of 49 fish species were registered in gillnets and 72 in fyke-nets. This projec represent the largest and longest time series on catches in gillnets and fyke-nets along the Danish coasts. As age and length and weight by age are followed on a regular basis it is possible to follow the development over time, to estimate if the population is in a healthy state.
ICES methods - 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. The data can be used to evaluate the development in the length and weight distribution for commercial species over time, as the gears are standardized between years.
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.
Description of the technical method is described in the Bathing Water Directive 2006/7/EC of 15 February 2006 Article 15 and must be in accordance with Annex I, IV and V in this Directive. Link enclosed: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:064:0037:0051:EN:PDF. Please find also a technical description of the method described in the Danish Statutory order (Statutory Order No. 2012-09-18. 939) concerning bathing and swimming areas. Reference to chapter 2 § 4/2. Link enclosed: https://www.retsinformation.dk/forms/R0710.aspx?id=143189. Attached is also a general technical description of measurement methods in the Danish Statutory Order (Statutory Order No. 231 of 05/03/2014) concerning quality standards for environmental measurements: https://www.retsinformation.dk/Forms/R0710.aspx?id=160496
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M03_CTD_maaling__VERSION_2_.pdf http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M04_Ilt_i_vandsoejlen.pdf http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M05_Fluorescens_ver1.pdf http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M06_Lyssvaekkelse_ver1.pdf
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_2_vandkemi.pdf
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_5_fytoplankton.pdf
The measurement methods are based on the methods recommended under the EMEP monitoring program. Part of the measurement methods has been slghtly modified compared to the EMPE methods. The modifications have been documented in connection with DCE's accriditation. The model calculations is based on DCE's air quality model called Danish hemispheric eulerian model.
Q9d - Description of alteration to method
The method can be seen in the manual.
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.
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.
This program is registering all birds by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch of breeding or wintering birds by is mainly registration if the bird is catch in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of birds.
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals.
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals.
The method can be seen in the manual. No age are estimated but length and weight. The data can be used to evaluate the development in the length and weight distribution for commercial species over time, as the gears are standardized.
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
  • National
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • BEQUALM
  • 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
  • COMBINE
  • National
  • see links included above
  • COMBINE
  • National
  • see link included above
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • National
  • see link with prject description: http://orbit.dtu.dk/files/100552186/Publishers_version.pdf
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • National
  • COMBINE
  • National
  • see links included above
  • see link included above
  • see link included above
  • EMEP standards
  • QUASIMEM
Q9f - Quality control
DelayedValidation
RealandDelayedValidation
RealandDelayedValidation
RealandDelayedValidation
RealandDelayedValidation
RealandDelayedValidation
DelayedValidation
OtherQC
OtherQC
OtherQC
OtherQC
OtherQC
OtherQC
DelayedValidation
RealandDelayedValidation
RealandDelayedValidation
RealandDelayedValidation
DelayedValidation
RealandDelayedValidation
RealandDelayedValidation
Unknown
DelayedValidation
Q9g - Spatial resolution of sampling Q9g - Proportion of area covered %
0.3
2.5
0.67
50
100
90
100
90
100
10
100
100
0.67
0.67
0.67
0.3
0.67
100
100
100
100
Q9g - Spatial resolution of sampling Q9g - No. of samples
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
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
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 species for age.
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.
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.
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 species for age.
Both model calculations and measurements covers the entire callendar year.
Q9i - Description of sample representivity
103 fishermen are participating with 3 sites eac. Indicating that each site represent 0.3% of the total. In total 52,000 individuals were caught in the last three year. Eelpout topped the list of species most frequently caught, mostly in fyke-nets. Next on the list was flounder with 23,000 individuals being caught over 3 years. An equal number of cod and eel were caught; 9,000 individuals. The catches reflect the fac.
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.
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
103 fishermen are participating with 3 sites eac. Indicating that each site represent 0.3% of the total. In total 52,000 individuals were caught in the last three year. Eelpout topped the list of species most frequently caught, mostly in fyke-nets. Next on the list was flounder with 23,000 individuals being caught over 3 years. An equal number of cod and eel were caught; 9,000 individuals. The catches reflect the fac.
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.
According to EU Directive 2006/7 / EC of 15 February 2006 on bathing water quality, sample taking will only take place in the "bathing season" (Denmark 1. of June to 1. of September / in some cases to 15. of September) and only were there are a "large number" of bathers. Link to Directive: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:064:0037:0051:EN:PDF. Please find also link to the Danish Statutory order concerning bathing water: https://www.retsinformation.dk/forms/R0710.aspx?id=143189. Please find link to the Reporting Sheet from EEA (European Environment Agency) : http://rod.eionet.europa.eu/obligations/531.
Q10a - Scale for aggregation of data
  • Subregion
  • Region
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Region
  • Subregion
  • EU
  • 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.
Q10c - Access to monitoring data Q10c - Data type
ProcessedData
Simulated
Simulated
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
ProcessedData
ProcessedData
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData
Simulated
ProcessedData DataProducts
UnprocessedData
UnprocessedData
UnprocessedData
ProcessedData
ProcessedData Simulated
Q10c - Access to monitoring data Q10c - Data access mechanism
LocationNationalDC
LocationInternationalDC
LocationInternationalDC
LocationInternationalDC
LocationInternationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationNationalDC
LocationInternationalDC
LocationInternationalDC
LocationInternationalDC
LocationNationalDC
LocationInternationalDC
LocationInternationalDC
LocationInternationalDC
URLview
LocationNationalDC
LocationNationalDC
LocationInternationalDC
Q10c - Access to monitoring data Q10c - Data access rights
RestrictedSpecific
RestrictedSpecific
RestrictedSpecific
Open
RestrictedSpecific
RestrictedSpecific
Open
Open
Open
Open
Open
Open
Open
Open
Open
RestrictedSpecific
RestrictedSpecific
RestrictedSpecific
RestrictedSpecific
RestrictedSpecific
RestrictedSpecific
Open
Open
Open
Open
Open
Q10c - Access to monitoring data Q10c - INSPIRE standard
OceanographicFeatures SeaRegions SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
OceanographicFeatures SpeciesDistribution
OceanographicFeatures SpeciesDistribution
HabitatsBiotopes SpeciesDistribution
OceanographicFeatures
HabitatsBiotopes SpeciesDistribution
SeaRegions SpeciesDistribution
HabitatsBiotopes SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
HabitatsBiotopes SeaRegions SpeciesDistribution
HabitatsBiotopes SeaRegions SpeciesDistribution
OceanographicFeatures SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
HabitatsBiotopes SpeciesDistribution
HabitatsBiotopes SeaRegions SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
OceanographicFeatures SpeciesDistribution
OceanographicFeatures SeaRegions SpeciesDistribution
EnvMonitoringFacilities
Hydrography OceanographicFeatures SeaRegions
OceanographicFeatures
OceanographicFeatures SeaRegions SpeciesDistribution
SeaRegions
Q10c - Access to monitoring data Q10c Date data are available
2015-10
2015-03
2015-03
2015-04
2015-04
2015-02
2015-12
2014-11
2014-11
2014-11
2014-11
2014-11
2014-11
2015-04
2015-04
2015-04
2015-04
2015-04
2015-10
2015-03
2015-04
2014-12
2014-12
2014-12
2015-04
2015-01
Q10c - Access to monitoring data Q10c - Data update frequency
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
6yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
2weekly
2weekly
Yearly
Yearly
Q10d - Description of data access
A national data base is holding the data.
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.
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
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.
http://www.miljoeportal.dk/Sider/Forside.aspx
http://www.miljoeportal.dk/Sider/Forside.aspx
In ICES Regional data base (RDB).
In ICES Regional data base (RDB).
In ICES Regional data base (RDB).
A national data base is holding the data.
ICES is presently working on constructing a database where all aquatic data can be uploaded and stored. Presently DTU Aqua is hosting this database.
In ICES Regional data base (RDB).
Data is sent to the EC / EEA by the end of December each year.
http://www.miljoeportal.dk/Sider/Forside.aspx
http://www.miljoeportal.dk/Sider/Forside.aspx
http://www.miljoeportal.dk/Sider/Forside.aspx
The data will be reported in yearly reports under the National Monitorn Prramme for Water and Nature, as well as in the forthcoming MSFD Art. 8 initial assessment due in 2018.