Member State report / Art11 / 2014 / D3 / Baltic
| Report type | Member State report to Commission |
| MSFD Article | Art. 11 Monitoring programmes (and Art. 17 updates) |
| Report due | 2014-10-15 |
| GES Descriptor | D3 Commercial fish and shellfish |
| Region/subregion | Baltic |
| Reported by | Reporter not found |
| Member state | DE |
DE |
DE |
DE |
DE |
DE |
DK |
DK |
DK |
DK |
DK |
DK |
DK |
DK |
DK |
DK |
DK |
DK |
DK |
FI |
FI |
FI |
FI |
FI |
LT |
LT |
LT |
LT |
LV |
LV |
LV |
LV |
LV |
LV |
LV |
LV |
LV |
LV |
PL |
PL |
SE |
SE |
SE |
SE |
SE |
SE |
SE |
SE |
SE |
SE |
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| Monitoring programme | Monitoring programme name | MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D1_4_6_SeabedHabitats |
MP_D1_4_6_SeabedHabitats |
MP_D1_4_6_SeabedHabitats |
MP_D1_4_6_SeabedHabitats |
MP_D1_4_6_SeabedHabitats |
MP_D1_4_6_SeabedHabitats |
MP_D1_4_6_SeabedHabitats |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D7 |
MP_D1_4_6_Fish |
MP_D1_4_6_Fish |
MP_D1_4_6_Fish |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D2 |
MP_D2 |
MP_D2 |
MP_D2 |
MP_D2 |
MP_D2 |
MP_D2 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D1_4_6_Mammals |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
| Monitoring programme | Reference existing programme | BALFI-D01,04,06fis |
BALFI-D01,04,06fis |
BALFI-D01,04,06fis |
Baltic International Trawl Surveys (BITS) |
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| Monitoring programme | Marine Unit ID |
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| Q4e - Programme ID | BALDE_Mon_020 |
BALDE_Mon_020 |
BALDE_Mon_020 |
BALDE_Mon_020 |
BALDE_Mon_020 |
BALDE_Mon_020 |
BALDK-D01,04,06 |
BALDK-D01,04,06 |
BALDK-D01,04,06 |
BALDK-D01,04,06 |
BALDK-D01,04,06 |
BALDK-D01,04,06 |
BALDK-D01,04,06 |
BALDK-D03 |
BALDK-D03 |
BALDK-D03 |
BALDK-D03 |
BALDK-D03 |
BALDK-D07 |
BALFI-D01,04,06fis |
BALFI-D01,04,06fis |
BALFI-D01,04,06fis |
BALFI-D03 |
BALFI-D03 |
BALLT-D01234-2 |
BALLT-D01234-2 |
BALLT-D01234-2 |
BALLT-D01234-2 |
BAL-LV-2014 |
BAL-LV-2014 |
BAL-LV-2014 |
BAL-LV-2014 |
BAL-LV-2014 |
BAL-LV-2014 |
BAL-LV-2014 |
BAL-LV-2014 |
BAL-LV-2014 |
BAL-LV-2014 |
BALPL-D0104_Mammals |
BALPL-D03 |
BALSE-COMFISH-D3 |
BALSE-COMFISH-D3 |
BALSE-COMFISH-D3 |
BALSE-COMFISH-D3 |
BALSE-COMFISH-D3 |
BALSE-COMFISH-D3 |
BALSE-COMFISH-D3 |
BALSE-COMFISH-D3 |
BALSE-COMFISH-D3 |
BALSE-COMFISH-D3 |
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| Q4f - Programme description |
Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen und Freizeitfischerei (Ostsee). Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die auswikrung von Fischerei (D3).
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Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen und Freizeitfischerei (Ostsee). Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die auswikrung von Fischerei (D3).
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Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen und Freizeitfischerei (Ostsee). Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die auswikrung von Fischerei (D3).
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Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen und Freizeitfischerei (Ostsee). Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die auswikrung von Fischerei (D3).
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Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen und Freizeitfischerei (Ostsee). Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die auswikrung von Fischerei (D3).
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Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen und Freizeitfischerei (Ostsee). Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die auswikrung von Fischerei (D3).
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"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework:
• State of habitats (habitat for species, extent, suitability)
• Mortality rates from anthropogenic activities
• Distribution and extent (incl. habitat forming species and biogenic reefs)
• Physical characteristics (topography, bathymetry, organics, oxygen levels)
• Community characteristics (species composition, abundance and/or biomass)
• Benthic species (species composition, abundance, coverage)
• Physical loss –dredging and disposal of dredged materials
• Pysical disturbance from bottom trawling
• Extracting non-living ressources |
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework:
• State of habitats (habitat for species, extent, suitability)
• Mortality rates from anthropogenic activities
• Distribution and extent (incl. habitat forming species and biogenic reefs)
• Physical characteristics (topography, bathymetry, organics, oxygen levels)
• Community characteristics (species composition, abundance and/or biomass)
• Benthic species (species composition, abundance, coverage)
• Physical loss –dredging and disposal of dredged materials
• Pysical disturbance from bottom trawling
• Extracting non-living ressources |
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework:
• State of habitats (habitat for species, extent, suitability)
• Mortality rates from anthropogenic activities
• Distribution and extent (incl. habitat forming species and biogenic reefs)
• Physical characteristics (topography, bathymetry, organics, oxygen levels)
• Community characteristics (species composition, abundance and/or biomass)
• Benthic species (species composition, abundance, coverage)
• Physical loss –dredging and disposal of dredged materials
• Pysical disturbance from bottom trawling
• Extracting non-living ressources |
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework:
• State of habitats (habitat for species, extent, suitability)
• Mortality rates from anthropogenic activities
• Distribution and extent (incl. habitat forming species and biogenic reefs)
• Physical characteristics (topography, bathymetry, organics, oxygen levels)
• Community characteristics (species composition, abundance and/or biomass)
• Benthic species (species composition, abundance, coverage)
• Physical loss –dredging and disposal of dredged materials
• Pysical disturbance from bottom trawling
• Extracting non-living ressources |
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework:
• State of habitats (habitat for species, extent, suitability)
• Mortality rates from anthropogenic activities
• Distribution and extent (incl. habitat forming species and biogenic reefs)
• Physical characteristics (topography, bathymetry, organics, oxygen levels)
• Community characteristics (species composition, abundance and/or biomass)
• Benthic species (species composition, abundance, coverage)
• Physical loss –dredging and disposal of dredged materials
• Pysical disturbance from bottom trawling
• Extracting non-living ressources |
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework:
• State of habitats (habitat for species, extent, suitability)
• Mortality rates from anthropogenic activities
• Distribution and extent (incl. habitat forming species and biogenic reefs)
• Physical characteristics (topography, bathymetry, organics, oxygen levels)
• Community characteristics (species composition, abundance and/or biomass)
• Benthic species (species composition, abundance, coverage)
• Physical loss –dredging and disposal of dredged materials
• Pysical disturbance from bottom trawling
• Extracting non-living ressources |
"The monitoring programme for seabed habitats consists of subprogrammes that fulfils the main parts of the DPSIR causal framework:
• State of habitats (habitat for species, extent, suitability)
• Mortality rates from anthropogenic activities
• Distribution and extent (incl. habitat forming species and biogenic reefs)
• Physical characteristics (topography, bathymetry, organics, oxygen levels)
• Community characteristics (species composition, abundance and/or biomass)
• Benthic species (species composition, abundance, coverage)
• Physical loss –dredging and disposal of dredged materials
• Pysical disturbance from bottom trawling
• Extracting non-living ressources |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches. |
The oceanographical monitoring programme of the Danish Meteorological Institute, DMI measures water level, tides, water temperature and currents that provide data for the forecast models of the DMI institute. The data supplements the general marine data collected in the framework of the existing environmental monitoring and is included in the marine models being developed under the National Monitoring Programme for Water and Nature, NOVANA.
In the present BALDK-D07 programme on hydrological changes extraction operations are included as these may cause hydrographical changes.
Major infrastructure works such as the fortcoming fixed link between Denmark and Germany is not included in the MSFD programme. A separate programme will be developed to control and monitor environmental status in relation to the environmental targets stipulated in the forthcoming Construction Bill for the fixed link across Fehmarn, |
General information is available in the HELCOM Monitoring manual (Biodiversity, Fish) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Fish
General information on Sub-programmes (Fish and Fisheries) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/ |
General information is available in the HELCOM Monitoring manual (Biodiversity, Fish) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Fish
General information on Sub-programmes (Fish and Fisheries) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/ |
General information is available in the HELCOM Monitoring manual (Biodiversity, Fish) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Fish
General information on Sub-programmes (Fish and Fisheries) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/ |
General information on monitoring of fish and fisheries is available at:
HELCOM Monitoring manual - Monitoring of “Fish, fisheries and shellfish” - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/
HELCOM Monitoring manual Sub-program: Coastal fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual Sub-program: Migratory fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish
HELCOM Monitoring manual Sub-program: Offshore fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
General information on monitoring of fish and fisheries is available at:
HELCOM Monitoring manual - Monitoring of “Fish, fisheries and shellfish” - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/
HELCOM Monitoring manual Sub-program: Coastal fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual Sub-program: Migratory fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish
HELCOM Monitoring manual Sub-program: Offshore fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
Duomenys šiems rodikliams renkami pagal Lietuvos nacionalinės žuvininkystės duomenų rinkimo programą (ES duomenų rinkimo programos, DCF). Tikslas - rinkti ir tvarkyti ES žvejybos ištekliams ir žuvininkystės sektoriui įvertinti reikalingus biologinius duomenis, duomenis apie žvejybos sektoriaus poveikį jūrų ekosistemai bei vykdyti mokslinius tyrimus jūroje. Verslinių žuvų išteklių vertinimas atliekamas pagal standartizuotą metodiką jau kelis dešimtmečius (ICES), ilgos laiko eilutės bei įvairių šalių patirtis ir kooperacija keičiantis informacija apie žuvų populiacijų parametrus užtikrina duomenų palyginamumą laiko skalėje bei įgalina susieti tai su pagrindiniu poveikiu – žvejybos intensyvumu. Metodika taip pat yra periodiškai peržiūrima (ICES).
Duomenų tikslumo lygiai ir ėminių ėmimo intensyvumas nustatytas 2009 m. gruodžio 18 d. Komisijos sprendimu Nr. 2010/93/ES. Be to, periodiškai teikiami pasiūlymai, rekomendacijos dėl žuvininkystės duomenų surinkimo schemų, metodikų, dalinamasi įgyvendinimo patirtimi, analizuojami/apdorojami surinkti visų šalių duomenys.
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Duomenys šiems rodikliams renkami pagal Lietuvos nacionalinės žuvininkystės duomenų rinkimo programą (ES duomenų rinkimo programos, DCF). Tikslas - rinkti ir tvarkyti ES žvejybos ištekliams ir žuvininkystės sektoriui įvertinti reikalingus biologinius duomenis, duomenis apie žvejybos sektoriaus poveikį jūrų ekosistemai bei vykdyti mokslinius tyrimus jūroje. Verslinių žuvų išteklių vertinimas atliekamas pagal standartizuotą metodiką jau kelis dešimtmečius (ICES), ilgos laiko eilutės bei įvairių šalių patirtis ir kooperacija keičiantis informacija apie žuvų populiacijų parametrus užtikrina duomenų palyginamumą laiko skalėje bei įgalina susieti tai su pagrindiniu poveikiu – žvejybos intensyvumu. Metodika taip pat yra periodiškai peržiūrima (ICES).
Duomenų tikslumo lygiai ir ėminių ėmimo intensyvumas nustatytas 2009 m. gruodžio 18 d. Komisijos sprendimu Nr. 2010/93/ES. Be to, periodiškai teikiami pasiūlymai, rekomendacijos dėl žuvininkystės duomenų surinkimo schemų, metodikų, dalinamasi įgyvendinimo patirtimi, analizuojami/apdorojami surinkti visų šalių duomenys.
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Duomenys šiems rodikliams renkami pagal Lietuvos nacionalinės žuvininkystės duomenų rinkimo programą (ES duomenų rinkimo programos, DCF). Tikslas - rinkti ir tvarkyti ES žvejybos ištekliams ir žuvininkystės sektoriui įvertinti reikalingus biologinius duomenis, duomenis apie žvejybos sektoriaus poveikį jūrų ekosistemai bei vykdyti mokslinius tyrimus jūroje. Verslinių žuvų išteklių vertinimas atliekamas pagal standartizuotą metodiką jau kelis dešimtmečius (ICES), ilgos laiko eilutės bei įvairių šalių patirtis ir kooperacija keičiantis informacija apie žuvų populiacijų parametrus užtikrina duomenų palyginamumą laiko skalėje bei įgalina susieti tai su pagrindiniu poveikiu – žvejybos intensyvumu. Metodika taip pat yra periodiškai peržiūrima (ICES).
Duomenų tikslumo lygiai ir ėminių ėmimo intensyvumas nustatytas 2009 m. gruodžio 18 d. Komisijos sprendimu Nr. 2010/93/ES. Be to, periodiškai teikiami pasiūlymai, rekomendacijos dėl žuvininkystės duomenų surinkimo schemų, metodikų, dalinamasi įgyvendinimo patirtimi, analizuojami/apdorojami surinkti visų šalių duomenys.
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Duomenys šiems rodikliams renkami pagal Lietuvos nacionalinės žuvininkystės duomenų rinkimo programą (ES duomenų rinkimo programos, DCF). Tikslas - rinkti ir tvarkyti ES žvejybos ištekliams ir žuvininkystės sektoriui įvertinti reikalingus biologinius duomenis, duomenis apie žvejybos sektoriaus poveikį jūrų ekosistemai bei vykdyti mokslinius tyrimus jūroje. Verslinių žuvų išteklių vertinimas atliekamas pagal standartizuotą metodiką jau kelis dešimtmečius (ICES), ilgos laiko eilutės bei įvairių šalių patirtis ir kooperacija keičiantis informacija apie žuvų populiacijų parametrus užtikrina duomenų palyginamumą laiko skalėje bei įgalina susieti tai su pagrindiniu poveikiu – žvejybos intensyvumu. Metodika taip pat yra periodiškai peržiūrima (ICES).
Duomenų tikslumo lygiai ir ėminių ėmimo intensyvumas nustatytas 2009 m. gruodžio 18 d. Komisijos sprendimu Nr. 2010/93/ES. Be to, periodiškai teikiami pasiūlymai, rekomendacijos dėl žuvininkystės duomenų surinkimo schemų, metodikų, dalinamasi įgyvendinimo patirtimi, analizuojami/apdorojami surinkti visų šalių duomenys.
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The monitoring programme is incomplete at the present stage due to lack of knowledge and severe limitation in indicator availability. Therefore, balance between parts of the monitoring programme can not be assessed |
The monitoring programme is incomplete at the present stage due to lack of knowledge and severe limitation in indicator availability. Therefore, balance between parts of the monitoring programme can not be assessed |
The monitoring programme is incomplete at the present stage due to lack of knowledge and severe limitation in indicator availability. Therefore, balance between parts of the monitoring programme can not be assessed |
It is expected that the mammals monitoring programme will include acoustic monitoring as performed in SAMBAH project, in addition for seals there will be an on line monitoring via CCD-TV and additional imaginery from air could be applied. |
The assessment of commercially exploited fish is performed in the frame of BITS surveys. At this stage the only assessed stocks are: cod, 2 flounder stocks, sprat and herring. There is still a need to set a monitoring programme in transitional waters and obtaining new data for the assessment of salmon, trout, and percisid species. |
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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| Q5e - Natural variability |
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| Q5d - Adequacy for assessment of GES | Q5d - Adequate data | Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
N |
N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
Y |
Y |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
| Q5d - Adequacy for assessment of GES | Q5d - Established methods | N |
N |
N |
N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
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 |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
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 |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
| Q5f - Description of programme for GES assessment |
Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhabl von D3.
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Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhabl von D3.
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Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhabl von D3.
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Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhabl von D3.
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Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhabl von D3.
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Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhabl von D3.
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The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values. |
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values. |
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values. |
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values. |
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values. |
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values. |
The programme provides data on key indicators for descriptor 1 and 4 and 6 . Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values. |
According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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The general programme provides information to assess possible alternations og the physical environment. Th extration activity is regulated in detail in Statutory Order no. 1169 issued 3/10-2013. In addition to this separate programmes are prepared in relation to possible large scale construction activities at sea based on EIA-assessments. |
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability. |
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability. |
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability. |
As reported for Art. 9 and 10, the threshold values for GES are:
The level of pressure of the fishing activity is not exceeding MSY-level, and the reproductive capacity of the fish populations is secured.
Both sub-programmes under this programme are sufficient to produce data on target species populations which are under international regulation. The data, which is collected within the sub-programmes, gives reliable information on population dynamics caused by fishing and natural factors. The program provides information for the descriptor 3 (MSD-criteria 3.1, 3.2 and 3.3), and as for salmon, for the descriptor 1 (MSD criteria 1.2 and 1.3). The program also collects information on fishing pressure. |
As reported for Art. 9 and 10, the threshold values for GES are:
The level of pressure of the fishing activity is not exceeding MSY-level, and the reproductive capacity of the fish populations is secured.
Both sub-programmes under this programme are sufficient to produce data on target species populations which are under international regulation. The data, which is collected within the sub-programmes, gives reliable information on population dynamics caused by fishing and natural factors. The program provides information for the descriptor 3 (MSD-criteria 3.1, 3.2 and 3.3), and as for salmon, for the descriptor 1 (MSD criteria 1.2 and 1.3). The program also collects information on fishing pressure. |
Šis deskriptorius taikomas visoms išteklių grupėms, kurios patenka į Reglamento (EB) Nr. 199/2008 (atsižvelgiant į Direktyvos 2008/56/EB geografinę aprėptį) ir panašių bendrosios žuvininkystės politikos reikalavimų taikymo sritį. Jo taikymas šioms ir kitoms išteklių grupėms priklauso nuo prieinamų duomenų (atsižvelgiant į Reglamento (EB) Nr. 199/2008 nuostatas dėl duomenų rinkimo), pagal kuriuos pasirenkami tinkamiausi naudotini rodikliai. Šio deskriptoriaus rodiklių kategorijos ir susiję rodikliai, pagal kuriuos vertinama pažanga, padaryta siekiant užtikrinti gerą aplinkos būklę. Šiame etape pagrindinėms komerciniams tikslams naudojamų žuvų rūšims (menkei, strimelei, brėtlingiui bei plekšnei) parengti trys rodikliai: mirtingumo dėl žvejybos koeficientas, didesnių už pirmą lytinės brandos normą žuvų proporcija ir 95 ilgio pasiskirstymo procentilis.
Rodikliai gerai atspindi žuvų bendrijų pokyčius. Atspindi komercinės žvejybos poveikio stiprumą eksploatuojamoms populiacijoms. Pagal pateikiamus nacionalinius duomenis, rodiklį skaičiuoja ICES ekspertai. Tyrimams paimama žuvų populiacijos dalis yra labai maža lyginant su visa populiacija. Rodikliai skaičiuojami ne Lietuvos teritorijai atskirai o konkrečios rūšies išteklių grupei (t.y. visai Baltijos jūrai (bretlingiui) ar jos daliai (menkei ir strimelei)
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Šis deskriptorius taikomas visoms išteklių grupėms, kurios patenka į Reglamento (EB) Nr. 199/2008 (atsižvelgiant į Direktyvos 2008/56/EB geografinę aprėptį) ir panašių bendrosios žuvininkystės politikos reikalavimų taikymo sritį. Jo taikymas šioms ir kitoms išteklių grupėms priklauso nuo prieinamų duomenų (atsižvelgiant į Reglamento (EB) Nr. 199/2008 nuostatas dėl duomenų rinkimo), pagal kuriuos pasirenkami tinkamiausi naudotini rodikliai. Šio deskriptoriaus rodiklių kategorijos ir susiję rodikliai, pagal kuriuos vertinama pažanga, padaryta siekiant užtikrinti gerą aplinkos būklę. Šiame etape pagrindinėms komerciniams tikslams naudojamų žuvų rūšims (menkei, strimelei, brėtlingiui bei plekšnei) parengti trys rodikliai: mirtingumo dėl žvejybos koeficientas, didesnių už pirmą lytinės brandos normą žuvų proporcija ir 95 ilgio pasiskirstymo procentilis.
Rodikliai gerai atspindi žuvų bendrijų pokyčius. Atspindi komercinės žvejybos poveikio stiprumą eksploatuojamoms populiacijoms. Pagal pateikiamus nacionalinius duomenis, rodiklį skaičiuoja ICES ekspertai. Tyrimams paimama žuvų populiacijos dalis yra labai maža lyginant su visa populiacija. Rodikliai skaičiuojami ne Lietuvos teritorijai atskirai o konkrečios rūšies išteklių grupei (t.y. visai Baltijos jūrai (bretlingiui) ar jos daliai (menkei ir strimelei)
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Šis deskriptorius taikomas visoms išteklių grupėms, kurios patenka į Reglamento (EB) Nr. 199/2008 (atsižvelgiant į Direktyvos 2008/56/EB geografinę aprėptį) ir panašių bendrosios žuvininkystės politikos reikalavimų taikymo sritį. Jo taikymas šioms ir kitoms išteklių grupėms priklauso nuo prieinamų duomenų (atsižvelgiant į Reglamento (EB) Nr. 199/2008 nuostatas dėl duomenų rinkimo), pagal kuriuos pasirenkami tinkamiausi naudotini rodikliai. Šio deskriptoriaus rodiklių kategorijos ir susiję rodikliai, pagal kuriuos vertinama pažanga, padaryta siekiant užtikrinti gerą aplinkos būklę. Šiame etape pagrindinėms komerciniams tikslams naudojamų žuvų rūšims (menkei, strimelei, brėtlingiui bei plekšnei) parengti trys rodikliai: mirtingumo dėl žvejybos koeficientas, didesnių už pirmą lytinės brandos normą žuvų proporcija ir 95 ilgio pasiskirstymo procentilis.
Rodikliai gerai atspindi žuvų bendrijų pokyčius. Atspindi komercinės žvejybos poveikio stiprumą eksploatuojamoms populiacijoms. Pagal pateikiamus nacionalinius duomenis, rodiklį skaičiuoja ICES ekspertai. Tyrimams paimama žuvų populiacijos dalis yra labai maža lyginant su visa populiacija. Rodikliai skaičiuojami ne Lietuvos teritorijai atskirai o konkrečios rūšies išteklių grupei (t.y. visai Baltijos jūrai (bretlingiui) ar jos daliai (menkei ir strimelei)
|
Šis deskriptorius taikomas visoms išteklių grupėms, kurios patenka į Reglamento (EB) Nr. 199/2008 (atsižvelgiant į Direktyvos 2008/56/EB geografinę aprėptį) ir panašių bendrosios žuvininkystės politikos reikalavimų taikymo sritį. Jo taikymas šioms ir kitoms išteklių grupėms priklauso nuo prieinamų duomenų (atsižvelgiant į Reglamento (EB) Nr. 199/2008 nuostatas dėl duomenų rinkimo), pagal kuriuos pasirenkami tinkamiausi naudotini rodikliai. Šio deskriptoriaus rodiklių kategorijos ir susiję rodikliai, pagal kuriuos vertinama pažanga, padaryta siekiant užtikrinti gerą aplinkos būklę. Šiame etape pagrindinėms komerciniams tikslams naudojamų žuvų rūšims (menkei, strimelei, brėtlingiui bei plekšnei) parengti trys rodikliai: mirtingumo dėl žvejybos koeficientas, didesnių už pirmą lytinės brandos normą žuvų proporcija ir 95 ilgio pasiskirstymo procentilis.
Rodikliai gerai atspindi žuvų bendrijų pokyčius. Atspindi komercinės žvejybos poveikio stiprumą eksploatuojamoms populiacijoms. Pagal pateikiamus nacionalinius duomenis, rodiklį skaičiuoja ICES ekspertai. Tyrimams paimama žuvų populiacijos dalis yra labai maža lyginant su visa populiacija. Rodikliai skaičiuojami ne Lietuvos teritorijai atskirai o konkrečios rūšies išteklių grupei (t.y. visai Baltijos jūrai (bretlingiui) ar jos daliai (menkei ir strimelei)
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There is a linkage between sub-programmes and descriptors provided in monitoring programme. However, the monitoring programme at present stage is incomplete due to lack of knowledge and correspondingly insufficient number of available indicators. At this time there is no or only very few indicators for descriptors 1, 4 and 6. Some ongoing work will result in HELCOM CORE set indicators for biodiversity that would be used for D1. However, indicator description is not yet finished. Therefore, it is not possible to assess how well adopted monitoring programme will contribute to assessment needs by use of developed indicators. Consequently, the need to amend monitoring programme is already foreseen. |
There is a linkage between sub-programmes and descriptors provided in monitoring programme. However, the monitoring programme at present stage is incomplete due to lack of knowledge and correspondingly insufficient number of available indicators. At this time there is no or only very few indicators for descriptors 1, 4 and 6. Some ongoing work will result in HELCOM CORE set indicators for biodiversity that would be used for D1. However, indicator description is not yet finished. Therefore, it is not possible to assess how well adopted monitoring programme will contribute to assessment needs by use of developed indicators. Consequently, the need to amend monitoring programme is already foreseen. |
There is a linkage between sub-programmes and descriptors provided in monitoring programme. However, the monitoring programme at present stage is incomplete due to lack of knowledge and correspondingly insufficient number of available indicators. At this time there is no or only very few indicators for descriptors 1, 4 and 6. Some ongoing work will result in HELCOM CORE set indicators for biodiversity that would be used for D1. However, indicator description is not yet finished. Therefore, it is not possible to assess how well adopted monitoring programme will contribute to assessment needs by use of developed indicators. Consequently, the need to amend monitoring programme is already foreseen. |
The monitoing programme will provide data for the assessment of relevant indicators. |
The programme is designed to provide adeqate data on commertially exploited species. Data will provide information on the trends of state for the relevant descriptors and for some stocks there is a GES boundary for the descriptors. |
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
|
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
|
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
|
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
|
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
|
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet
d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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| Q5g - Gap-filling date for GES assessment | By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
By2014 |
By2014 |
By2014 |
By2020 |
By2020 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
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| Q5h - Plans to implement monitoring for GES assessment |
Aufgrund von unzureichenden Daten liegen nicht für alle genutzten Bestände analytische Bewertungen vor, so dass derzeit nicht für alle Bestände ermittelt werden kann, ob sie nach dem MSY-Prinzip befischt werden. Es gibt aber vielversprechende Ansätze innerhalb der angewandten Fischereiforschung für die Bewertung dieser datenärmeren Bestände. Wie eine Bewertung des Längenkriteriums unter D3 aussehen könnte, ist gegenwärtig unklar. Hierzu wird jedoch auf internationaler Ebene (ICES) geforscht.
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Aufgrund von unzureichenden Daten liegen nicht für alle genutzten Bestände analytische Bewertungen vor, so dass derzeit nicht für alle Bestände ermittelt werden kann, ob sie nach dem MSY-Prinzip befischt werden. Es gibt aber vielversprechende Ansätze innerhalb der angewandten Fischereiforschung für die Bewertung dieser datenärmeren Bestände. Wie eine Bewertung des Längenkriteriums unter D3 aussehen könnte, ist gegenwärtig unklar. Hierzu wird jedoch auf internationaler Ebene (ICES) geforscht.
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Aufgrund von unzureichenden Daten liegen nicht für alle genutzten Bestände analytische Bewertungen vor, so dass derzeit nicht für alle Bestände ermittelt werden kann, ob sie nach dem MSY-Prinzip befischt werden. Es gibt aber vielversprechende Ansätze innerhalb der angewandten Fischereiforschung für die Bewertung dieser datenärmeren Bestände. Wie eine Bewertung des Längenkriteriums unter D3 aussehen könnte, ist gegenwärtig unklar. Hierzu wird jedoch auf internationaler Ebene (ICES) geforscht.
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Aufgrund von unzureichenden Daten liegen nicht für alle genutzten Bestände analytische Bewertungen vor, so dass derzeit nicht für alle Bestände ermittelt werden kann, ob sie nach dem MSY-Prinzip befischt werden. Es gibt aber vielversprechende Ansätze innerhalb der angewandten Fischereiforschung für die Bewertung dieser datenärmeren Bestände. Wie eine Bewertung des Längenkriteriums unter D3 aussehen könnte, ist gegenwärtig unklar. Hierzu wird jedoch auf internationaler Ebene (ICES) geforscht.
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Aufgrund von unzureichenden Daten liegen nicht für alle genutzten Bestände analytische Bewertungen vor, so dass derzeit nicht für alle Bestände ermittelt werden kann, ob sie nach dem MSY-Prinzip befischt werden. Es gibt aber vielversprechende Ansätze innerhalb der angewandten Fischereiforschung für die Bewertung dieser datenärmeren Bestände. Wie eine Bewertung des Längenkriteriums unter D3 aussehen könnte, ist gegenwärtig unklar. Hierzu wird jedoch auf internationaler Ebene (ICES) geforscht.
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Aufgrund von unzureichenden Daten liegen nicht für alle genutzten Bestände analytische Bewertungen vor, so dass derzeit nicht für alle Bestände ermittelt werden kann, ob sie nach dem MSY-Prinzip befischt werden. Es gibt aber vielversprechende Ansätze innerhalb der angewandten Fischereiforschung für die Bewertung dieser datenärmeren Bestände. Wie eine Bewertung des Längenkriteriums unter D3 aussehen könnte, ist gegenwärtig unklar. Hierzu wird jedoch auf internationaler Ebene (ICES) geforscht.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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Please see section “Jūras monitoringa programmas nepilnību novēršanas plāns” in monitoring programme.
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Please see section “Jūras monitoringa programmas nepilnību novēršanas plāns” in monitoring programme.
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Please see section “Jūras monitoringa programmas nepilnību novēršanas plāns” in monitoring programme.
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Filling of gaps in data and assessment methods.
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
||||||||||||||||||||||||||
| Q6a -Relevant targets | Q6a - Environmental target | UZO3 UZO4 |
UZO3 UZO4 |
UZO3 UZO4 |
UZO3 UZO4 |
UZO3 UZO4 |
UZO3 UZO4 |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_13_BAL DK_23_BAL DK_36_BAL |
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18 |
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18 |
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18 |
Target 12 Target 13 Target 14 Target 15 Target 16 |
Target 12 Target 13 Target 14 Target 15 Target 16 |
3 |
3 |
3 |
3 |
Target 1 Target 6 |
Target 1 Target 6 |
Target 1 Target 6 |
Target 1 Target 6 |
Target 1 Target 6 |
Target 1 Target 6 |
Target 1 Target 6 |
Target 2 |
Target 2 |
Target 2 |
C.3 C.4 |
C.3 C.4 |
C.3 C.4 |
C.3 C.4 |
C.3 C.4 |
C.3 C.4 |
C.3 C.4 |
C.3 C.4 |
C.3 C.4 |
C.3 C.4 |
||
| Q6a -Relevant targets | Q6a - Associated indicator | UZO3_IND_3.2.3 UZO4_IND_4.1.1 UZO4_IND_4.1.2 UZO4_IND_4.2.1 UZO4_IND_4.2.2 |
UZO3_IND_3.2.3 UZO4_IND_4.1.1 UZO4_IND_4.1.2 UZO4_IND_4.2.1 UZO4_IND_4.2.2 |
UZO3_IND_3.2.3 UZO4_IND_4.1.1 UZO4_IND_4.1.2 UZO4_IND_4.2.1 UZO4_IND_4.2.2 |
UZO3_IND_3.2.3 UZO4_IND_4.1.1 UZO4_IND_4.1.2 UZO4_IND_4.2.1 UZO4_IND_4.2.2 |
UZO3_IND_3.2.3 UZO4_IND_4.1.1 UZO4_IND_4.1.2 UZO4_IND_4.2.1 UZO4_IND_4.2.2 |
UZO3_IND_3.2.3 UZO4_IND_4.1.1 UZO4_IND_4.1.2 UZO4_IND_4.2.1 UZO4_IND_4.2.2 |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_4_BAL DK_9_BAL DK_11_BAL DK_12_BAL DK_13_BAL DK_20_BAL DK_22_BAL DK_24_BAL DK_25_BAL DK_35_BAL DK_36_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL |
DK_13_BAL DK_23_BAL DK_36_BAL |
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18 |
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18 |
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18 |
Target 12 Target 13 Target 14 Target 15 Target 16 |
Target 12 Target 13 Target 14 Target 15 Target 16 |
3.1.1 a 3.1.1 b 3.1.1 c 3.3.3 a 3.3.3 b 3.3.3 c 3.3.3 d |
3.1.1 a 3.1.1 b 3.1.1 c 3.3.3 a 3.3.3 b 3.3.3 c 3.3.3 d |
3.1.1 a 3.1.1 b 3.1.1 c 3.3.3 a 3.3.3 b 3.3.3 c 3.3.3 d |
3.1.1 a 3.1.1 b 3.1.1 c 3.3.3 a 3.3.3 b 3.3.3 c 3.3.3 d |
||||||||||||||||||||||
| Q6b - Adequacy for assessment of targets | Q6b_SuitableData | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
| Q6b - Adequacy for assessment of targets | Q6b_EstablishedMethods | N |
N |
N |
N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
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 |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
| Q6c - Target updating | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
||||||||
| Q6d - Description of programme for targets assessment |
Auch wenn die derzeitige Bewertung von Fischbeständen noch Lücken aufweist, werden die methodischen Innovationen und vorhandenen Daten eine repräsentative Bewertung der fischereilichen Nutzung erlauben. Es fehlen noch Bewertungsmethoden für datenarme Bestände sowie für das Längenkriterium unter D3.
|
Auch wenn die derzeitige Bewertung von Fischbeständen noch Lücken aufweist, werden die methodischen Innovationen und vorhandenen Daten eine repräsentative Bewertung der fischereilichen Nutzung erlauben. Es fehlen noch Bewertungsmethoden für datenarme Bestände sowie für das Längenkriterium unter D3.
|
Auch wenn die derzeitige Bewertung von Fischbeständen noch Lücken aufweist, werden die methodischen Innovationen und vorhandenen Daten eine repräsentative Bewertung der fischereilichen Nutzung erlauben. Es fehlen noch Bewertungsmethoden für datenarme Bestände sowie für das Längenkriterium unter D3.
|
Auch wenn die derzeitige Bewertung von Fischbeständen noch Lücken aufweist, werden die methodischen Innovationen und vorhandenen Daten eine repräsentative Bewertung der fischereilichen Nutzung erlauben. Es fehlen noch Bewertungsmethoden für datenarme Bestände sowie für das Längenkriterium unter D3.
|
Auch wenn die derzeitige Bewertung von Fischbeständen noch Lücken aufweist, werden die methodischen Innovationen und vorhandenen Daten eine repräsentative Bewertung der fischereilichen Nutzung erlauben. Es fehlen noch Bewertungsmethoden für datenarme Bestände sowie für das Längenkriterium unter D3.
|
Auch wenn die derzeitige Bewertung von Fischbeständen noch Lücken aufweist, werden die methodischen Innovationen und vorhandenen Daten eine repräsentative Bewertung der fischereilichen Nutzung erlauben. Es fehlen noch Bewertungsmethoden für datenarme Bestände sowie für das Längenkriterium unter D3.
|
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 1, 4 and 6. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 7. Togehter with existing data series information on variability, trends and distances from levels recorded previously the programme will provide data for assessing possible progress towards reaching targets. |
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report) |
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report) |
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report) |
The progress towards the targets will be monitored by a number of indicators. |
The progress towards the targets will be monitored by a number of indicators. |
Vertinimus atlieka ICES.
|
Vertinimus atlieka ICES.
|
Vertinimus atlieka ICES.
|
Vertinimus atlieka ICES.
|
The monitoring programme is incomplete at the present stage due to lack of knowledge and severe limitation in indicator availability. The indicators are lacking as well as system/tool to aggregate the indicator-based assessments so that the overall progress towards targets could be assessed.
Question 6a: The assessment system that agregates indicators to assess targets is not developped yet. The target values are elaborated for separate indicators. Information on that can be found in document elaborated for Initial assessment (www.lhei.lv/docs/2012/Juras_derektiva_C.pdf) |
The monitoring programme is incomplete at the present stage due to lack of knowledge and severe limitation in indicator availability. The indicators are lacking as well as system/tool to aggregate the indicator-based assessments so that the overall progress towards targets could be assessed.
Question 6a: The assessment system that agregates indicators to assess targets is not developped yet. The target values are elaborated for separate indicators. Information on that can be found in document elaborated for Initial assessment (www.lhei.lv/docs/2012/Juras_derektiva_C.pdf) |
The monitoring programme is incomplete at the present stage due to lack of knowledge and severe limitation in indicator availability. The indicators are lacking as well as system/tool to aggregate the indicator-based assessments so that the overall progress towards targets could be assessed.
Question 6a: The assessment system that agregates indicators to assess targets is not developped yet. The target values are elaborated for separate indicators. Information on that can be found in document elaborated for Initial assessment (www.lhei.lv/docs/2012/Juras_derektiva_C.pdf) |
The monitoing programme will provide data for the assessment of relevant targets. |
Programme is designed to provide frequent data on the changes in the commercialy exploited fish stocks which will enable the adequate estimation of the progress towards targets. |
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
|
||||||||
| Q6e - Gap-filling date for targets assessment | By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
By2020 |
By2020 |
By2020 |
By2020 |
By2020 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
|
| Q6f - Plans to implement monitoring for targets assessment |
Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern.
Es fehlen noch Bewertungmethoden für datenarme Bestände, für die in der angeandten Fischereiforschung vielversprechende Ansätze gibt. Es ist zu erwarten, dass bis 2018 einige dieser Methoden Eingang in das ICES-Bewertungsystem finden werden.
|
Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern.
Es fehlen noch Bewertungmethoden für datenarme Bestände, für die in der angeandten Fischereiforschung vielversprechende Ansätze gibt. Es ist zu erwarten, dass bis 2018 einige dieser Methoden Eingang in das ICES-Bewertungsystem finden werden.
|
Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern.
Es fehlen noch Bewertungmethoden für datenarme Bestände, für die in der angeandten Fischereiforschung vielversprechende Ansätze gibt. Es ist zu erwarten, dass bis 2018 einige dieser Methoden Eingang in das ICES-Bewertungsystem finden werden.
|
Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern.
Es fehlen noch Bewertungmethoden für datenarme Bestände, für die in der angeandten Fischereiforschung vielversprechende Ansätze gibt. Es ist zu erwarten, dass bis 2018 einige dieser Methoden Eingang in das ICES-Bewertungsystem finden werden.
|
Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern.
Es fehlen noch Bewertungmethoden für datenarme Bestände, für die in der angeandten Fischereiforschung vielversprechende Ansätze gibt. Es ist zu erwarten, dass bis 2018 einige dieser Methoden Eingang in das ICES-Bewertungsystem finden werden.
|
Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern.
Es fehlen noch Bewertungmethoden für datenarme Bestände, für die in der angeandten Fischereiforschung vielversprechende Ansätze gibt. Es ist zu erwarten, dass bis 2018 einige dieser Methoden Eingang in das ICES-Bewertungsystem finden werden.
|
Please see section “Jūras monitoringa programmas nepilnību novēršanas plāns” in monitoring programme.
|
Please see section “Jūras monitoringa programmas nepilnību novēršanas plāns” in monitoring programme.
|
Please see section “Jūras monitoringa programmas nepilnību novēršanas plāns” in monitoring programme.
|
Filling of gaps in data and methods used.
|
Filling gaps in data and assessment methods.
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
|
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| Q7a - Relevant activities |
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| Q7b - Description of monitoring of activities |
Das Monitoring zu D3 bezieht sich auf die kommerzielle und nicht-kommerzielle (Freizeit-)Fischerei.
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Das Monitoring zu D3 bezieht sich auf die kommerzielle und nicht-kommerzielle (Freizeit-)Fischerei.
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Das Monitoring zu D3 bezieht sich auf die kommerzielle und nicht-kommerzielle (Freizeit-)Fischerei.
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Das Monitoring zu D3 bezieht sich auf die kommerzielle und nicht-kommerzielle (Freizeit-)Fischerei.
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Das Monitoring zu D3 bezieht sich auf die kommerzielle und nicht-kommerzielle (Freizeit-)Fischerei.
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Das Monitoring zu D3 bezieht sich auf die kommerzielle und nicht-kommerzielle (Freizeit-)Fischerei.
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The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed |
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed |
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed |
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed |
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed |
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed |
The programme provides data on key indicators of the seabed habitat together with the relevant pressures impacting the biodiversity and habitat quality of the sed bed |
According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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The programme provides data on key hydrological indicators including pressures impacting the hydrological quality. Extraction of nonliving ressources is regulated in detail in Staturoy Order no. 1169 issued 3/10-2013. |
No monitoring of activities
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No monitoring of activities
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No monitoring of activities
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Fishery is widespread activity impacting primarily target fish stocks. It also affects other fish stocks, sea-birds and marine mammals due to by-catch. In Finnish waters there are no bottom touching fishing gears in use.
Fishery data is collected via EU data collection framework and catch statistics by the fishermen from the whole region. |
Fishery is widespread activity impacting primarily target fish stocks. It also affects other fish stocks, sea-birds and marine mammals due to by-catch. In Finnish waters there are no bottom touching fishing gears in use.
Fishery data is collected via EU data collection framework and catch statistics by the fishermen from the whole region. |
Pagrinde atspindi žvejybos intensyvumą.
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Pagrinde atspindi žvejybos intensyvumą.
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Pagrinde atspindi žvejybos intensyvumą.
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Pagrinde atspindi žvejybos intensyvumą.
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•The land-based pressure monitoring is addressed in the frame of Water framework directive.
•Atmospheric depositions of nutrients and selected contaminants are addressed on regional level through cooperation in HELCOM frame. The actual calculations are performed by EMEP and presented for the whole regional in form of maps.
•The ship traffic intensity as well as oil pollution by ships is addressed in form of regional cooperation in HELCOM. Oil spill maps are regularly updated and published on HELCOM web page covering whole region.
•Fishing pressure is addressed in the frame of CFP.
•The physical impact by port activities (dumping of dredged material, maintenance of port facilities) and potentially impact by construction of other infrastructure is and will be addressed locally in frame of Impact assessment procedure and following operator monitoring.
•The marine litter will be addressed on regional scale. Currently HELCOM Marine litter action plan, that will include also suggestions on monitoring, is in elaboration stage.
•Noise is not addressed at present. |
•The land-based pressure monitoring is addressed in the frame of Water framework directive.
•Atmospheric depositions of nutrients and selected contaminants are addressed on regional level through cooperation in HELCOM frame. The actual calculations are performed by EMEP and presented for the whole regional in form of maps.
•The ship traffic intensity as well as oil pollution by ships is addressed in form of regional cooperation in HELCOM. Oil spill maps are regularly updated and published on HELCOM web page covering whole region.
•Fishing pressure is addressed in the frame of CFP.
•The physical impact by port activities (dumping of dredged material, maintenance of port facilities) and potentially impact by construction of other infrastructure is and will be addressed locally in frame of Impact assessment procedure and following operator monitoring.
•The marine litter will be addressed on regional scale. Currently HELCOM Marine litter action plan, that will include also suggestions on monitoring, is in elaboration stage.
•Noise is not addressed at present. |
•The land-based pressure monitoring is addressed in the frame of Water framework directive.
•Atmospheric depositions of nutrients and selected contaminants are addressed on regional level through cooperation in HELCOM frame. The actual calculations are performed by EMEP and presented for the whole regional in form of maps.
•The ship traffic intensity as well as oil pollution by ships is addressed in form of regional cooperation in HELCOM. Oil spill maps are regularly updated and published on HELCOM web page covering whole region.
•Fishing pressure is addressed in the frame of CFP.
•The physical impact by port activities (dumping of dredged material, maintenance of port facilities) and potentially impact by construction of other infrastructure is and will be addressed locally in frame of Impact assessment procedure and following operator monitoring.
•The marine litter will be addressed on regional scale. Currently HELCOM Marine litter action plan, that will include also suggestions on monitoring, is in elaboration stage.
•Noise is not addressed at present. |
The programme will give direct linkage to information on the pressere from fisheries as well as on the intensity of underwater noise. |
The programme is estimating the condition of commercially exploited fish in a yearly manner. The data on commertially axploited fish is collected once a year. |
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
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| Q7c - Relevant measures | |||||||||||||||||||||||||||||||||||||||||||||||||||
| Q7e - Adequacy for assessment of measures | Q7d - Adequate data | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
Y |
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| Q7e - Adequacy for assessment of measures | Q7d - Established methods | Y |
Y |
Y |
Y |
N |
N |
N |
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| Q7e - Adequacy for assessment of measures | Q7d - Adequate understanding of GES | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
Y |
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| Q7e - Adequacy for assessment of measures | Q7d - Adequate capacity | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
Y |
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| Q7e - Adequacy for assessment of measures | Q7d - Addresses activities and pressures | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
N |
Y |
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| Q7e - Adequacy for assessment of measures | Q7d - Addresses effectiveness of measures | N |
N |
N |
N |
N |
N |
Y |
Y |
Y |
Y |
N |
N |
N |
Y |
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| Q7d - Description of monitoring for measures |
Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018.
Das derzeitige Monitoring von D3 erlaubt eine regelmäßige Bestandsbewertung der Hauptzielarten. Das Spektrum der bewerteten Arten wird durch neue Bewertungsansätze in Zukunft noch breiter und somit noch repräsentativer werden. Die Bestandsbewertungen erlauben die Einschätzung, wie viele der genutzten Bestände entsprechend den MSY-Zielen genutzt werden.
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Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018.
Das derzeitige Monitoring von D3 erlaubt eine regelmäßige Bestandsbewertung der Hauptzielarten. Das Spektrum der bewerteten Arten wird durch neue Bewertungsansätze in Zukunft noch breiter und somit noch repräsentativer werden. Die Bestandsbewertungen erlauben die Einschätzung, wie viele der genutzten Bestände entsprechend den MSY-Zielen genutzt werden.
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Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018.
Das derzeitige Monitoring von D3 erlaubt eine regelmäßige Bestandsbewertung der Hauptzielarten. Das Spektrum der bewerteten Arten wird durch neue Bewertungsansätze in Zukunft noch breiter und somit noch repräsentativer werden. Die Bestandsbewertungen erlauben die Einschätzung, wie viele der genutzten Bestände entsprechend den MSY-Zielen genutzt werden.
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Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018.
Das derzeitige Monitoring von D3 erlaubt eine regelmäßige Bestandsbewertung der Hauptzielarten. Das Spektrum der bewerteten Arten wird durch neue Bewertungsansätze in Zukunft noch breiter und somit noch repräsentativer werden. Die Bestandsbewertungen erlauben die Einschätzung, wie viele der genutzten Bestände entsprechend den MSY-Zielen genutzt werden.
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Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018.
Das derzeitige Monitoring von D3 erlaubt eine regelmäßige Bestandsbewertung der Hauptzielarten. Das Spektrum der bewerteten Arten wird durch neue Bewertungsansätze in Zukunft noch breiter und somit noch repräsentativer werden. Die Bestandsbewertungen erlauben die Einschätzung, wie viele der genutzten Bestände entsprechend den MSY-Zielen genutzt werden.
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Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018.
Das derzeitige Monitoring von D3 erlaubt eine regelmäßige Bestandsbewertung der Hauptzielarten. Das Spektrum der bewerteten Arten wird durch neue Bewertungsansätze in Zukunft noch breiter und somit noch repräsentativer werden. Die Bestandsbewertungen erlauben die Einschätzung, wie viele der genutzten Bestände entsprechend den MSY-Zielen genutzt werden.
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Monitoring of measures is not part of National environmental monitoring programme. Measures and their monitoring will be addressed in coming Programme of measures. |
Monitoring of measures is not part of National environmental monitoring programme. Measures and their monitoring will be addressed in coming Programme of measures. |
Monitoring of measures is not part of National environmental monitoring programme. Measures and their monitoring will be addressed in coming Programme of measures. |
The programme is estimating the condition of commercially exploited fish in a yearly manner. The data on commertially axploited fish is collected once a year. |
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| 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 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
After2020 |
By2020 |
By2020 |
By2020 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
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| Q8a - Links to existing Monitoring Programmes |
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| Reference sub-programme | Sub-programme ID | BALDK-D01-22_seabed_distribution |
BALDK-D06-02_abundance_hardbottom |
BALDK-D06-03_abundance_softbottomflora |
BALDK-D06-04_abundance_softbottomfauna |
BALDK-D06-06_physidisturb_trawl |
BALDK-D03-04_mortal_fisheries_birds |
BALDK-D03-05_mortal_fisheries_porpoise |
BALDK-D03-06_mortal_fisheries_seals |
BALDK-D03-08_mortal_fish_coastal |
BALDK-D03-10_mortal_fish_offsh_commercial |
BALFI-D01,04,06fis-1 |
BALFI-D01,04,06fis-2 |
BALFI-D01,04,06fis-3 |
BALFI-D03-1 |
BALFI-D03-2 |
BALLT-D01234_FishOffshore |
BALLT-D01234_FishOffshore |
BALLT-D01234_FishOffshore |
BALLT-D01234_FishOffshore |
BALPL-D0104-Mammals |
BALPL-D03-01 |
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| Reference sub-programme | Sub-programme name | Mobile species - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Seabed habitats - community characteristics |
Physical disturbance - from dredging and disposal of dredged material |
Seabed habitats - physical/chemical characteristics |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Physical disturbance - from bottom trawling |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Activities extracting non-living resources (sand, gravel, dredging) |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Activities extracting living resources (fisheries including recreational, maerl, seaweed) |
Activities extracting living resources (fisheries including recreational, maerl, seaweed) |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Pelagic habitats - community characteristics |
Plankton blooms (biomass, frequency) |
Seabed habitats - community characteristics |
Benthic species - abundance and/or biomass |
Seabed habitats - distribution and extent |
Non-indigenous species - abundance and/or biomass |
Non-indigenous species inputs - from specific sources |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - population characteristics |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Benthic species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
| Q4g - Sub-programmes | Sub-programme ID | BALDK-D01-22_seabed_distribution |
BALDK-D06-02_abundance_hardbottom |
BALDK-D06-03_abundance_softbottomflora |
BALDK-D06-04_abundance_softbottomfauna |
BALDK-D06-06_physidisturb_trawl |
BALDK-D03-04_mortal_fisheries_birds |
BALDK-D03-05_mortal_fisheries_porpoise |
BALDK-D03-06_mortal_fisheries_seals |
BALDK-D03-08_mortal_fish_coastal |
BALDK-D03-10_mortal_fish_offsh_commercial |
BALFI-D01,04,06fis-1 |
BALFI-D01,04,06fis-2 |
BALFI-D01,04,06fis-3 |
BALFI-D03-1 |
BALFI-D03-2 |
BALLT-D01234_FishOffshore |
BALLT-D01234_FishOffshore |
BALLT-D01234_FishOffshore |
BALLT-D01234_FishOffshore |
BALPL-D0104-Mammals |
BALPL-D03-01 |
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| Q4g - Sub-programmes | Sub-programme name | Mobile species - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Seabed habitats - community characteristics |
Physical disturbance - from dredging and disposal of dredged material |
Seabed habitats - physical/chemical characteristics |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Physical disturbance - from bottom trawling |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Activities extracting non-living resources (sand, gravel, dredging) |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Activities extracting living resources (fisheries including recreational, maerl, seaweed) |
Activities extracting living resources (fisheries including recreational, maerl, seaweed) |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Pelagic habitats - community characteristics |
Plankton blooms (biomass, frequency) |
Seabed habitats - community characteristics |
Benthic species - abundance and/or biomass |
Seabed habitats - distribution and extent |
Non-indigenous species - abundance and/or biomass |
Non-indigenous species inputs - from specific sources |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - population characteristics |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Benthic species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
| Q4k - Monitoring purpose | StateImpact |
StateImpact |
StateImpact |
StateImpact |
Activities |
Activities |
Activities |
Activities |
StateImpact |
Activities |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact Pressurse Activities Measures |
StateImpact Pressurse Activities Measures |
StateImpact Pressurse Activities Measures |
StateImpact Pressurse Activities Measures |
StateImpact Pressurse Activities |
StateImpact Pressurse Activities |
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| Q4l - Links of monitoring programmes of other Directives and Conventions | There are no specific technical descriptions of the methods behing the distribution maps. It takes place in two phases - mapping of bottom substrates using either side scan sonar or multibeam sonar and surveys of the biological compositions of the areas using videosurveys. Definitions of the habitattypes follows a habitattype description written by the Danish Nature Agency in coorperation with DCE.
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/Biodiversitet/Habitat-beskrivelser-app4b-ver104_opdatering-havtyper2012.pdf. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.4 and figur 8.7 shows the position of the stations. 60% of the stations are in the BALDK area and 40% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ .
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.3 shows the position of the stations. 70% of the stations are in the BALDK area and 30% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.5 shows the position of the stations. 60% of the stations are in the BALDK area and 40% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive,Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
DTU Aqua has access to VMS data from all Danish commercial vessels from 2005 (above 15 meters) and from 2012 (above 12 meters). VMS data has been linked to logbook data and can therefore show pressure on the seabed by gear and target species.The access is to all Danish vessels within this size category in all waters. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
Catches from the recreational fisheries are registered on a voluntary basis by ”key” fishermen at fixed stations in most parts of the Danish coasts. The catches are performed with standard gillnets (one mesh size, 65 mm) and/or fyke nets, with up to 3 samples monthly in the beginning of each month, and from around April to November. Because of the mesh size used, the gillnets sample mostly adults, whereas juveniles of flounder and cod may be caught in the fyke nets. At present about 100+ fishers are invovled in the project. the last report with a detailed description can be downloaded:
http://orbit.dtu.dk/files/100552186/Publishers_version.pdf |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
Not relevant
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Essential information describing this national sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish |
Essential information describing this national sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish |
Essential information describing this national sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
Essential information describing this national sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
Common Fisheries Policy
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Common Fisheries Policy
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Common Fisheries Policy
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Common Fisheries Policy
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Hydro acoustic monitoring of Harbour porpoise is based on the SAMBAH project. Other aspects are included in Polish Monitoring Programme through
http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf |
http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf
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| Q5c - Features | Q5c - Habitats |
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| Q5c - Features | Q5c - Species list |
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| Q5c - Features | Q5c - Physical/Chemical features |
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| Q5c - Features | Q5c - Pressures |
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| Q9a - Elements |
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| Q5a - GES criteria | Relevant GES criteria |
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| Q5b - GES indicators | Relevant GES indicators |
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| Q9b - Parameters monitored (state/impact) | Species distribution |
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| Q9b - Parameters monitored (state/impact) | Species population size |
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| Q9b - Parameters monitored (state/impact) | Species population characteristics |
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| Q9b - Parameters monitored (state/impact) | Species impacts |
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| Q9b - Parameters monitored (state/impact) | Habitat distribution |
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| Q9b - Parameters monitored (state/impact) | Habitat extent |
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| Q9b - Parameters monitored (state/impact) | Habitat condition (physical-chemical) |
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| Q9b - Parameters monitored (state/impact) | Habitat condition (biological) |
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| Q9b - Parameters monitored (state/impact) | Habitat impacts |
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| Q9b - Parameters monitored (pressures) | Pressure input | ||||||||||||||||||||||||||||||||||||||||||||||||||
| Q9b - Parameters monitored (pressures) | Pressure output |
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| Q9b - Parameters monitored (activity) | Activity |
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| Q9b Parameters monitored (other) | Other | ||||||||||||||||||||||||||||||||||||||||||||||||||
| Q41 Spatial scope | WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
WFD_CW |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW |
WFD_CW EEZ BeyondMSwaters |
WFD_CW |
WFD_TW |
WFD_CW |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
EEZ |
EEZ |
EEZ |
EEZ |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
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| Q4j - Description of spatial scope | The monitoring is not systematic. Larger scale distribution mapping of reefs and sandbanks started in 2011.
Mapping takes place within Natura 2000 areas and specific mapping of deep muddy bottom and shallow mud surfaces are not mapped. |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions. |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions. |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions. |
The vessel monitoring system (VMS) is a satellite-based monitoring system which at regular intervals provides data to the fisheries authorities on the location, course and speed of vessels. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
The aim of the "Key-fishermen" projects is to register fish catches and document fish assemblages in Danish coastal waters over a consecutive number of years. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
The sub-programme monitors in the sea the structure of the river-spawning White Fish populations, which migrate to spawn in the rivers of the Bothnian Bay. |
HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish |
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish |
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
Monitoring is carried out according requirements under Common Fisheries Policy. |
Monitoring is carried out according requirements under Common Fisheries Policy. |
Monitoring is carried out according requirements under Common Fisheries Policy. |
Monitoring is carried out according requirements under Common Fisheries Policy. |
The pilot programme aims to reflect state of higle mobile species which occure in the whole Polish EEZ of the Baltic Sea. |
The data for the programme will be available from BITS surveys |
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| Marine Unit IDs |
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| Q4h - Temporal scope | Start date- End date | - |
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2011-9999 |
1990-9999 |
1987-9999 |
1990-9999 |
2005-9999 |
1995-9999 |
1995-9999 |
1995-9999 |
2005-9999 |
1995-9999 |
- |
1980-9999 |
1976-9999 |
1970-9999 |
1970-9999 |
1970-9999 |
1992-9999 |
1992-9999 |
1992-9999 |
1992-9999 |
- |
- |
- |
- |
- |
- |
- |
- |
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- |
2016-2018 |
2014-9999 |
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| Q9h - Temporal resolution of sampling |
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| Q9c - Monitoring method | Methods are described in the mapping reports such as the 2011 report which can be found here: http://www2.nst.dk/Download/Udgivelser/N2000_Marin_raastof_naturtypekort_kattegat_oestersoe_2011.pdf |
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del4/TA04_4_2_Haardbundsfauna.pdf |
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M12_Makroalger_paa_kystnaer_haard_bund__VERSION_2_.pdf |
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del4/TA04_4_1_Bloedbundsfauna.pdf |
http://icesjms.oxfordjournals.org/content/68/1/245.abstract |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
In this project 102 voluntary recreational fishermen participated, using either gillnets, fyke-nets or both gear types. Note that the results resented in this report represent catches reported by recreational fishermen. All species have caught have been registered and length measurements have been taken. The results showed a high fish biodiversity in Danish coastal waters. A total of 49 fish species were registered in gillnets and 72 in fyke-nets. This projec represent the largest and longest time series on catches in gillnets and fyke-nets along the Danish coasts. As age and length and weight by age are followed on a regular basis it is possible to follow the development over time, to estimate if the population is in a healthy state. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
Spawning Whitefish, migrating to rivers in September-October, are sampled from catches caught by local fishermen. Various fishing gear are used (e.g. net and fyke) to catch a few hundred individuals per river. The samplings take place 2-3 times during each spawning season. |
Sea trout parr are caught by electro fishing, after which they are tagged and released.
HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish |
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish |
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
ICES WGBFAS (Assessment WG), ICES WGBIFS (Survey WG)- https://datras.ices.dk/Documents/Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf - Manual for the Baltic International Trawl Surveys |
ICES WGBFAS (Assessment WG), ICES WGBIFS (Survey WG)- https://datras.ices.dk/Documents/Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf - Manual for the Baltic International Trawl Surveys |
ICES WGBFAS (Assessment WG), ICES WGBIFS (Survey WG)- https://datras.ices.dk/Documents/Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf - Manual for the Baltic International Trawl Surveys |
ICES WGBFAS (Assessment WG), ICES WGBIFS (Survey WG)- https://datras.ices.dk/Documents/Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf - Manual for the Baltic International Trawl Surveys |
http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf
Monitoring of grey seal is based on http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Guidelines%20for%20Seal%20Abundance%20Monitoring%20HELCOM%202014.pdf. The monitoring will include weekly aerial surveys along the polish coastline from March untill September 2016-2018. Data on the occurance and the data from video recording from the Vistula Mouth region will also be included.
Monitroing of Harbour porpoise will be performed as a continuation of Sambah project and will be performed once in the period 2016-2018. |
http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf
based on
https://datras.ices.dk/Documents/Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf |
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| Q9d - Description of alteration to method | Not relevant |
This program is registering all birds by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch of breeding or wintering birds by is mainly registration if the bird is catch in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of birds. |
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals. |
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals. |
The method can be seen in the manual. No age are estimated but length and weight. The data can be used to evaluate the development in the length and weight distribution for commercial species over time, as the gears are standardized. |
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| Q9e - Quality assurance |
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| Q9f - Quality control | RealandDelayedValidation |
DelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
DelayedValidation |
RealandDelayedValidation |
Unknown |
Unknown |
RealValidation |
Unknown |
Unknown |
DelayedValidation |
DelayedValidation |
DelayedValidation |
DelayedValidation |
OtherQC |
Unknown |
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| Q9g - Spatial resolution of sampling | Q9g - Proportion of area covered % | 2 |
2 |
2 |
0.3 |
2 |
15 |
100 |
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| Q9g - Spatial resolution of sampling | Q9g - No. of samples | Sidescan data is gatherered covering most of the bottom of the mapped Natura 2000 sites. Number of videosamles vary |
18% of the total vessels operating in this area were above 12 meters in 2013. |
around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected species for age. |
Around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected species for age. |
Around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected speces for age. |
around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected speces for age. |
Eight rivers in the Bothnian Bay. |
HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish |
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish |
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
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| 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. |
Information on the activity Fisheries is collected at HELCOM level. See under "Action areas" at: http://www.helcom.fi/action-areas |
The Grey seal monitoring will be performed weekly from March untill September 2016-2018.
Harbour porpoise will be monitored once in the time period 2016-2018 |
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| Q10a - Scale for aggregation of data |
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| Q10b - Other scale for aggregation of data | Currently the definitions of the habitat types are not agreed on between countries,. The definition fits within the definition described in the habitatsdirective, but could still vary from country to country. However, if other countries have similar maps produced an overall view of the the distribution of habitat types should be possible. Danish data is currently used for fisheries regulation in an international setting - where other countries have fishing rights in Danish waters. |
The only significant river spawning White Fish populations occur in the Bothnian Bay |
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| Q10c - Access to monitoring data | Q10c - Data type | ProcessedData DataProducts |
ProcessedData |
ProcessedData |
ProcessedData |
ProcessedData |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData DataProducts |
UnprocessedData ProcessedData |
UnprocessedData ProcessedData |
UnprocessedData ProcessedData |
UnprocessedData ProcessedData |
UnprocessedData |
UnprocessedData |
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| Q10c - Access to monitoring data | Q10c - Data access mechanism | URLdownload |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationNationalDC |
LocationInternationalDC |
LocationInternationalDC |
LocationInternationalDC |
LocationNationalDC |
LocationInternationalDC |
URLview |
URLview |
URLview |
URLview |
URLview |
LocationInternationalDC |
LocationInternationalDC |
LocationInternationalDC |
LocationInternationalDC |
URLdownload |
URLdownload |
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| Q10c - Access to monitoring data | Q10c - Data access rights | Open |
Open |
Open |
Open |
RestrictedSpecific |
Open |
Open |
Open |
RestrictedSpecific |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
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| Q10c - Access to monitoring data | Q10c - INSPIRE standard | HabitatsBiotopes OceanographicFeatures SpeciesDistribution |
HabitatsBiotopes SeaRegions SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes OceanographicFeatures |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
SpeciesDistribution |
SeaRegions SpeciesDistribution |
SpeciesDistribution |
SpeciesDistribution |
AquacultureFacilities ManagementZonesReportingUnits |
AquacultureFacilities ManagementZonesReportingUnits |
AquacultureFacilities ManagementZonesReportingUnits |
AquacultureFacilities ManagementZonesReportingUnits |
EnvMonitoringFacilities |
EnvMonitoringFacilities |
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| Q10c - Access to monitoring data | Q10c Date data are available | 2014-12 |
2015-04 |
2015-04 |
2015-04 |
2014-10 |
2015-04 |
2015-04 |
2015-04 |
2015-10 |
2015-04 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2011-06 |
2011-06 |
2011-06 |
2011-06 |
2017-01 |
2015-12 |
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| Q10c - Access to monitoring data | Q10c - Data update frequency | Yearly |
Yearly |
Yearly |
2yearly |
3monthly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
6yearly |
Yearly |
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| Q10d - Description of data access | All current mapping projects has been combined: http://miljoegis.mim.dk/cbkort?&profile=natura2000planer2basis2013 Additionally the individual mapping projects are available in separat paper reports such as:
http://www2.nst.dk/Download/Udgivelser/N2000_Marin_raastof_naturtypekort_kattegat_oestersoe_2011.pdfand as interactive URL sites: http://www2.naturstyrelsen.dk/habitatkortlaegning/ |
http://www.miljoeportal.dk/Sider/Forside.aspx, in addition aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
http://www.miljoeportal.dk/Sider/Forside.aspx, in addition aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
http://www.miljoeportal.dk/Sider/Forside.aspx.
In addition, aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is available and can be requested. As both logbook data and VMS data is realtime and online the data can be made available on request.
Do to the law on personal data, the data is only made available in aggregated form. In addition, aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB), as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB) as well as in the forthcoming MSFD art 8 initial assessment due in 2018.. |
In ICES Regional data base (RDB) as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
A national data base is holding the data, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB).as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data available by request from the Finnish Game and Fisheries Research Institute - http://www.rktl.fi/english/fish/fish_resources/whitefish_in_the_1.html |
HELCOM CORE indicator - Abundance of Sea Trout spawners and parr - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_sea_trout_spawners_and_parr.pdf
Data on tagged fish is available by request from Finnish Game and Fisheries Research Institute - http://www.rktl.fi/english/fish/fish_resources/
OIVA-open data service (in Finnish): https://wwwp2.ymparisto.fi/scripts/oiva.asp
More information on data access is available in the HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish |
HELCOM CORE indicator - Abundance of key fish species - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_key_fish_species.pdf
HELCOM CORE indicator - Abundance of fish key functional groups - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_fish_key_functional_groups.pdf
Public web service on environmental information OIVA (in Finnish) - www.ymparisto.fi/oiva
More information on data access is available in the HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish |
HELCOM CORE Indicator: Abundance of key fish species - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_key_fish_species.pdf
HELCOM CORE Indicator: Proportion of large fish in the community - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Proportion_of_large_fish_in_the_community.pdf
Essential information on data access is available in the HELCOM Monitoring manual:
- Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
- Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
HELCOM CORE Indicator: Abundance of key fish species - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_key_fish_species.pdf
HELCOM CORE Indicator: Proportion of large fish in the community - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Proportion_of_large_fish_in_the_community.pdf
Essential information on data access is available in the HELCOM Monitoring manual:
- Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
- Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish |
Monitoring data is located in Fisheries Service under the Ministry of the Agriculture (http://www.zuv.lt/index.php?1381214678). Organisation is responsible for data submission to international bodies |
Monitoring data is located in Fisheries Service under the Ministry of the Agriculture (http://www.zuv.lt/index.php?1381214678). Organisation is responsible for data submission to international bodies |
Monitoring data is located in Fisheries Service under the Ministry of the Agriculture (http://www.zuv.lt/index.php?1381214678). Organisation is responsible for data submission to international bodies |
Monitoring data is located in Fisheries Service under the Ministry of the Agriculture (http://www.zuv.lt/index.php?1381214678). Organisation is responsible for data submission to international bodies |
Since the programme for the monitoring of mammals is a pilot programme which is to be carried out in 2016-2018 the way of distributing information is not yet known. Most probably the data will become available through Helcom fascilities. |
EEA EIONET for WFD monitoring.
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