Member State report / Art11 / 2014 / D1-R / 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 | D1 Reptiles |
| Region/subregion | Baltic |
| Reported by | Reporter not found |
| Member state | DE |
DK |
FI |
LT |
LV |
PL |
SE |
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| Monitoring programme | Monitoring programme name | MP_D1_4_6_Birds |
MP_D1_4_6_Fish |
MP_D1_4_6_Mammals |
MP_D1_4_6_SeabedHabitats |
MP_D1_4_6_WaterColumnHabitats |
MP_D3 |
MP_D5 |
MP_D1_4_6_Birds |
MP_D1_4_6_Mammals |
MP_D1_4_6_SeabedHabitats |
MP_D3 |
MP_D5 |
MP_D8 |
MP_D1_4_6_Birds |
MP_D1_4_6_Fish |
MP_D1_4_6_Mammals |
MP_D1_4_6_SeabedHabitats |
MP_D3 |
MP_D1_4_6_Birds |
MP_D1_4_6_Fish |
MP_D2 |
MP_D5 |
MP_D1_4_6_Birds |
MP_D1_4_6_Fish |
MP_D1_4_6_Mammals |
MP_D1_4_6_WaterColumnHabitats |
MP_D2 |
MP_D1_4_6_Birds |
MP_D1_4_6_Fish |
MP_D1_4_6_Mammals |
MP_D3 |
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| Reference existing programme | BALFI-D01,04,06fis |
BALFI-D01,04,06ben |
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| Marine Unit ID |
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| Q4e - Programme ID | BALDE_Mon_014 |
BALDE_Mon_016 |
BALDE_Mon_015 |
BALDE_Mon_018 |
BALDE_Mon_017 |
BALDE_Mon_020 |
BALDE_MON_021 |
BALDK-birds-D01-04 |
BALDK-mammal-D01-04 |
BALDK-D01,04,06 |
BALDK-D03 |
BALDK-D05 |
BALDK-D08 |
BALFI-D01,04,06bir |
BALFI-D01,04,06fis |
BALFI-D01,04,06mam |
BALFI-D01,04,06ben |
BALFI-D03 |
BALLT-D018-3 |
BALLT-D01234-2 |
BAL-LV-2014 |
BAL-LV-2014 |
BALPL-D0104_Birds |
BALPL-D0104_Fish |
BALPL-D0104_Mammals |
BALPL-D0104_WaterColumnHabitats |
BALPL-D02 |
BALSE-Birds-D14 |
BALSE-Fish-D14 |
ANSSE-mammals-D14 |
BALSE-COMFISH-D3 |
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| Q4f - Programme description |
Das Monitoring der Biodiversität von Vögeln erfasst im wesentlich Abundanz, Verteilung und weitere ausgewählte biologische Parameter von Vogelarten. Das Monitoring überwacht somit hauptsächlich Zustände von Vogelpopulationen und -gemeinschaften. Erfasst und bewertet werden See- und Küstenvögel, i...
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Das Monitoring der Biodiversität von Fischen erfasst im wesentlichen die Abundanz und biologische Parameter einzelner Arten. Das Monitoring erfasst somit hauptsächlich Zustände in Fischpopulationen und Fischgemeinschaften. Belastungen, welche die Biodiversität von Fischen beeinflussen, werden in ...
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Das Monitoring der Biodiversität von Säugern erfasst im wesentlich Abundanz, Verteilung und weitere ausgewählte biologische Parameter der drei regelmäßig im Hoheitsgebiet vorkommenden Säugerarten (Seehund, Kegelrobbe, Schweinswal). Das Monitoring überwacht somit hauptsächlich Zustände ihrer Popul...
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Das Monitoringprogramm zielt auf die Überwachung der Fläche, Verbreitung und den Zustand der benthischen Habitate ab und damit indirekt auch auf die Abbildung der Belastung. Über den parallel begonnenen Prozess der Quantifizierung und Verortung der bestehenden Belastungen und menschlichen Aktivit...
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Das Monitoring der pelagischen Habitate umfasst die Planktongemeinschaften (Zoo- und Phytoplankton) einschließlich der Artenzusammensetzung, Abundanz und Biomasse. Die Belastungen werden im Rahmen des Eutrophierungsmonitorings erhoben. Über die Eutrophierungsbewertung von HELCOM (HEAT) und die HE...
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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 Eutrophierungsmonitoring berücksichtigt sowohl die Nährstoffeinträge (flussbürtig und atmosphärisch), die Nährstoffkonzentrationen als auch die direkten und indirekten Eutrophierungseffekte. Über die Eutrophierungsbewertung von HELCOM (HEAT) und die HELCOM PLC Berichterstattung werden untersc...
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Birds are generally well monitored in danish waters. The programme includes state/impact, pressures, activities and measures. Marine birds are primerely monitored as a functional group in MSFD context. All birds directive areas and other baltic sea areas are monitored. Monitoring is primerely focused on state (numbers and distribution). In case of relevant populations not beeing stabile or in progress further investigative monitoring will be initiated to identify causalities. |
All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable.
In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities. |
"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 eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data. |
The Programme for contaminants consists of subprogrammes that reflects the main concept of the DPSIR causal framework: Subprogrammes on health
• Health-breeding birds
• Health-fish demersal and coastal
• Health-hardbottomfauna
• Health-softbottomfauna
Subprogrammes on input
• Contaminant input from atmospheric deposition
• Contaminant input from sources at land
Subprogrammes on concentrations
• Contaminant level in water
• Contaminant level in biota
• Contaminant level in sediments
Subprogrammes on human activities extracting non-living resources
• Activities extracting non-living resources at sea |
General information is available in the HELCOM Monitoring manual (Biodiversity-Birds) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Birds
General information on Sub-programmes is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/ |
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 - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Mammals
General information on Sub-programs is available in the HELCOM Monitoring manual - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/ |
General information is available in the HELCOM Monitoring manual (Biodiversity - Seabed habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#SeabedHabitats
General information on Sub-programmes (Seabed habitat distribution and extent) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/ |
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 |
Paukščių monitoringo priekrantės zonoje bei atviros jūros vandenyse dėka vertinama Europos Bendrijos svarbos žiemojančių jūrinių paukščių rūšinė sudėtis, gausumas ir pasiskirstymas. Vertinant tik šalies mastu, indikatorius gali būti įtakojamas ilgalaikio paukščių žiemaviečių persiskirstymo, pvz. ...
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The aim is to make a reliable assessment of the state and composition of Lithuanian coastal fish communities, taking into account the diversity of communities, age structure of the main fish species, population parameters of abundance and biomass, as well as changes in populations and communities...
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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. |
http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf
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Polish Monitoring Programme covers all relevant aspects of MSFD. The programme is available through:
http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf |
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 Monitorng programme follows directly HELCOM COMBINE monitoring guidelines and is in line with MSFD reporting requirements. |
Data for the programme will be delivered from D1 and D4 descriptors. The monitoring programme is expected to be supported by additional data from the port surveys according to the paper:
HELCOM/OSPAR, 2013. Joint HELCOM/OSPAR Guidelines on the granting of exemptions under International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A-4 |
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats
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See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
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See programme Biologisk mångfald – Marina däggdjur (D1 och 4), 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 |
N |
Y |
N |
N |
Y |
Y |
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N |
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| Q5d - Established methods | N |
N |
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| Q5d - Adequate understanding of GES | Y |
Y |
Y |
Y |
N |
Y |
Y |
Y |
Y |
Y |
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| Q5d - Adequate capacity | N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
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| Q5f - Description of programme for GES assessment |
Im Rahmen des Monitorings werden alle anwesenden Vogelarten erfasst, so dass sowohl für jede einzelne Art Auswertungen (Abundanzen, Phänologien, Trends) als auch für funktionelle Gruppen vorgenommen werden können, so dass Statusänderungen auf Art- und Artengruppenebene, Auswirkungen von (neuen) B...
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Die Indikatoren entsprechend EU-KOM/477/2010 basieren überwiegend auf Abundanzerfassungen der Fischgemeinschaften. Derzeit sind Methoden zur Berechnung und Bewertung der Indikatoren noch in nationaler und internationaler Abstimmung, die notwendigen Daten stehen durch die seit meist Jahrzehnten be...
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Im Rahmen des Monitorings werden alle drei Säugerarten erfasst, so dass Auswertungen (Abundanzen, Phänologien, Trends), Statusänderungen und Auswirkungen von (neuen) Belastungen und Maßnahmen aufgezeigt und gegenüber natürlichen Schwankungen abgegrenzt werden können. Damit sind auch Rückschlüsse auf Habitatebene möglich.
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Die Benthosgemeinschaften werden habitatspezifisch mit bestimmten Indices bewertet. Wesentliche Parameter dieser Indices sind z.B. die Artenzusammensetzung, die Abundanz und bestimmte Charakteristika der benthischen Arten (Sensitivität, Indikation), die unter dem Gesichtspunkt Qualität/ Zustand o...
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Das Monitoring der pelagischen Habitate liefert Daten über Artenzusammensetzung, Abundanz, Gesamtbiomasse sowie Biomasse funktioneller Gruppen der vorherrschenden Phyto- und Zooplanktongemeinschaften. In Kombination mit den ebenfalls erhobenen Daten zu möglichen Belastungen werden darüber Teilaskpekte des Deskriptors Biodiversität sowie Nahrungsnetze abgedeckt.
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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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Mit dem Monitoring soll überprüft werden, ob die entsprechenden Maßnahmen zur Reduzierung der Eutrophierung führen und sich dies sowohl in den direkten als auch in den indirekten Eutrophierungseffekten zeigt. Diese können ebenso wie die Nährstoffkonzentrationen quantitativ bewertet werden, womit ...
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Link NOVANA.
Jagtstatistikker
Fugle-entusiaster indrapporterer observationer af fugle i en on-line database DOF-basen. Data dækker lokaliteter over hele landet, men med sparsom dækning på det marine område. Kystnære lokaliteter er derimod vel-repræsenterede.
DTU Aqua forvalter et program med ca...
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Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf.
Beredskabsplanen fo...
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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. |
According to coordination in ICES
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The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values. |
The programme provides answers to assessing the monitored values of the selected indicators in relation to Community legislation. |
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. |
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability. The monitoring of benthic fauna and flora is established; currently biotopes are being monitored through this monitoring. The Finnish underwater nature mapping program (VELMU) has mapped all benthic biotopes which serves as a baseline for monitoring of the remaining biotopes, which will be assessed by 2018 on the basis of this mapping. |
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. |
Monitoringo (apimančio žiemojančių jūros paukščių rūšinės sudėties, gausumo ir pasiskirstymo, apskaitos nuo kranto ir atviroje jūros dalyje) rezultatai bus pakankami jų panaudojimui jūros aplinkos būklei vertinti pagal naudojamą rodiklį – žiemojančių jūrinių paukščių populiacijos gausumas (1.2.1....
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The status of the Baltic Sea Coastal Fish Community is assessed on the basis of HELCOM recommendations using 4 key indicators reflecting the state of the fish communities: the Community Diversity Index (Shannon Index) (Indicator 1.6.1.), the Community Size Index (high fish abundance) (indicator 1...
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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. |
The Monitoring Programme will focus on three elements Waterbirds in wintering season, Waterbirds in breeding season and White tailed eagle and will cover all relevant regions and subregions. The data delivery will be sufficient. |
Programme will provide all data needed for the asseessment of relevant MSFD criteria and indicators. |
The monitoing programme will provide data for the assessment of relevant indicators. |
The programme is adequate and sufficient enough to provide data for the description of GES. |
Monitoring programme proviedes adeqate data for assessment needs of MSFD relevant Descriptors. Programme is designed to provide the information on distribution and occurance of non indigenous species in open waters as well as in relevant ports. |
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats and chapter Bedömning av tillräcklighet.
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a. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet, table
c. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet
d. See programme ...
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a. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet
b. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet
c. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillrä...
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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 ny...
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| Q5g - Gap-filling date for GES assessment | By2018 |
By2018 |
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By2014 |
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After2020 |
By2018 |
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By2014 |
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| Q5h - Plans to implement monitoring for GES assessment |
Weitere Methoden zur Berechnung und Bewertung der Indikatoren sind derzeit noch in nationaler und internationaler Abstimmung.
Nationale Vorhaben mit MSRL-Bezug insbesondere zu Bewertungsfragen sind gestartet.
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Die Berechnung und Bewertung der Indikatoren muss national und im Hinblick auf die Entwicklungen in den Meeresübereinkommen (HELCOM) abgestimmt und durchgeführt werden. Exemplarische Vorschläge liegen in Form von wissenschaftlichen Studien vor.
Für viele der deutschen Nahrungsnetz-Indikatoren we...
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Derzeit sind Methoden zur Berechnung und Bewertung der Indikatoren noch in nationaler und internationaler Abstimmung, die notwendigen Daten stehen durch die bereits langjährig bestehenden Messprogramme als Zeitreihen zur Verfügung. Es muss jedoch auf nationaler und internationaler Ebene (FFH/HELCOM) eine Abstimmung über das Vorgehen zur Bewertung erreicht werden.
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Es wird an der Erweiterung des Monitorings (weitere Stationen) zur räumlichen Abdeckung auch der 12 sm Zone und der Nutzung von Daten Dritter gearbeitet. Wesentlich ist die Kartierung sublitoraler Habitate in den nächsten Jahren und die Weiterentwicklung spezifischer Parameter für eine adäquate o...
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In den Küstengewässer wird das Phytoplanktonmonitoring seit vielen Jahren durchgeführt. Zooplanktonindikatoren befinden sich momentan in Entwicklung. Das Zooplanktonmonitoring wird in den Küstengewässern zukünftig parallel zur Indikatorenentwicklung an diese angepasst ausgebaut.
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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 f...
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Da das Eutrophierungsmonitoring bereits eine lange Historie hat gibt es nur wenige Lücken (z.B. Messung der Versauerung, atmosphärische Deposition von Phosphor etc.), die in den nächsten Jahren mit Hilfe von zum Teil bereits begonnen oder geplanten (Pilot-)Projekten geschlossen werden sollen. Ins...
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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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Benthic biotope monitoring will be further developed for the next monitoring cycle based on the baseline mapping. |
No immediate development needs.
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Nuo 2016 metų planuojama sudažninti žiemojančių paukščių monitoringą (vykdyti kas du metus) ir išplėsti tyrimų rajoną, įtraukiant stebėjimus teritorinėje jūroje/IEZ. Taip pat paukščių stebėsenos koordinavimas, o taip pat duomenų analizė vykdoma ir regioniniu mastu. Lietuvos ekspertai dalyvauja ta...
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Monitoring is scheduled to take place annually instead of 1 times every 3 years. The planned research sites will sufficiently cover the diversity of natural conditions in the area under assessment and the potential impact of human activities. Lithuanian experts participate in the regional (Baltic...
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Please see section “Jūras monitoringa programmas nepilnību novēršanas plāns” in monitoring programme.
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Filling gaps in data and assessment methods.
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The programme needs additional filling of gaps in data and assessment methods. |
Filling the gaps in data and methods used.
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See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser
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See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
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See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
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| Q6a -Relevant targets | Q6a - Environmental target | UZO3 |
UZO3 UZO4 |
UZO3 |
UZO3 |
UZO3 UZO4 |
UZO1 |
DK_7_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_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_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_15_BAL DK_26_BAL DK_38_BAL |
Target 01 Target 02 Target 04 Target 17 Target 30 |
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18 |
Target 01 Target 02 Target 03 Target 17 Target 30 |
Target 06 Target 07 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26 |
Target 12 Target 13 Target 14 Target 15 Target 16 |
4 |
4 |
Target 1 Target 6 |
Target 3 |
C.3 C.4 |
C.3 C.4 |
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| Q6a - Associated indicator | UZO3_IND_3.1.1 UZO3_IND_3.1.2 UZO3_IND_3.2.3 |
UZO3_IND_3.2.3 UZO3_IND_3.3.1 UZO4_IND_4.2.1 UZO4_IND_4.3.4 |
UZO3_IND_3.1.1 UZO3_IND_3.1.2 UZO3_IND_3.2.3 |
UZO3_IND_3.1.3 UZO3_IND_3.1.4 |
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 |
UZO1_IND_1.1.1 UZO1_IND_1.2.1 UZO1_IND_1.2.2 UZO1_IND_1.3.1 UZO1_IND_1.3.2 |
DK_7_BAL |
DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL |
DK_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_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL |
DK_15_BAL DK_38_BAL |
Target 01 Target 02 Target 04 Target 17 Target 30 |
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18 |
Target 01 Target 02 Target 03 Target 17 Target 30 |
Target 06 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26 |
Target 12 Target 13 Target 14 Target 15 Target 16 |
1.2.1 a 1.2.1 b 1.2.1 c 1.2.1 d 1.2.1 e 1.2.1 f 1.2.1 g 1.3.1 a |
1.6.1 1.7.1 4.2.1 a 4.2.1 b 4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f |
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| Q6b - Adequacy for assessment of targets | Q6b_SuitableData | Y |
N |
Y |
N |
N |
Y |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
Y |
Y |
Y |
Y |
Y |
N |
Y |
N |
Y |
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| Q6b_EstablishedMethods | N |
Y |
Y |
N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
Y |
N |
N |
N |
Y |
N |
Y |
N |
Y |
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| Q6d_AdequateCapacity | N |
Y |
Y |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
N |
Y |
Y |
N |
Y |
N |
Y |
Y |
Y |
Y |
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| Q6c - Target updating | Y |
Y |
Y |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
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| Q6d - Description of programme for targets assessment |
Durch die Erfassung der Vogelarten und die spezifische Zuordnung in funktionelle Gruppen wird das Monitoringprogramm eine Bewertung der Vogelgemeinschaften erlauben und damit zur Bewertung von Habitaten beitragen, was die Beurteilung der Erreichung der entprechenden deutschen Umweltzielen ermöglicht.
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Durch die Erfassung der Fischabundanzen ist die Grundlage für die Überprüfung der Umweltziele. Diese müssen jedoch für die Indikatoren noch spezifiziert werden. Diese Spezifikation wird im Rahmen der nationalen und internatoinalen Abstimmung bis 2018 statt finden.
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Durch die Erfassung der Säugerarten in ihren Jahreslebensräumen wird das Monitoringprogramm eine Bewertung auf Artebene erlauben und damit zur Bewertung von Habitaten beitragen, was die Beurteilung der Erreichung der entprechenden deutschen Umweltzielen ermöglicht.
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Um das Umweltziel „ 3.1..ausreichender Schutz und Rückzugsräume für Ökosystemkomponenten (…benthische Arten)“ zu erreichen muss mit der Überwachung die Habitatfläche, ihre Verteilung und der Zustand der benthischen Gemeinschaft abgebildet werden. Erst durch Einrichtung von Zonen ohne die menschli...
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Der Zustand der pelagischen Habitate ist im Wesentlichen durch Eutrophierung beeinträchtigt. Insofern wird davon ausgegangen, dass durch das Errreichen des Umweltziels 1 (Meere ohne Beeinträchtigung durch anthropogene Eutrophierung) auch der
gute Umweltzustand für pelagische Habitate erreicht wer...
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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.
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Mit dem Monitoring soll überprüft werden, ob die entsprechenden Maßnahmen zur Reduzierung der atmosphärischen Einträge, Flusseinträge und Ferneinträge führen und sich dies sowohl in den direkten als auch in den indirekten Eutrophierungseffekten zeigt.
Es bestehen keine Lücken und eine Aussage zur Zielerreichung ist mit dem vorliegenden Monitoring möglich.
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The programme provides data on key indicators for descriptor 1 and 4. Existing data series will enable computations on variability, trends and distances fro mlevels recorded earlier as well as provide data for the assessment of possible progress towards reaching targets. |
Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM.
Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf
Beredskabsplanen for...
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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 keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets. |
This programme provides data on key indicators for descriptor 8. Together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
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 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. |
2015 metais bus atnaujinti tikslai ir susiję pažangos vertinimo rodikliai, tuomet bus galima pakartotinai vertinti monitoringo rezultatų panaudojimą/programos adekvatumą.
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The status shall be assessed annually using monitoring data on the basis of indicators of good environmental status.
A revision of the objectives and related indicators is foreseen for 2015. The adequacy and adequacy of monitoring will then be assessed in order to assess progress towards objectives.
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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) |
Programme will deliver frequent (yearly) data on birds and assossiated attributes. |
The programme will deliver data needed for the assessment of progres with targets. |
The monitoing programme will provide data for the assessment of relevant targets. |
The programme will provide sufficient data.
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The programme will provide data on distribution of non indigenous species. |
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Bedömning av tillräcklighet
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See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet
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See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet
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See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
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| Q6e - Gap-filling date for targets assessment | By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
After2020 |
By2018 |
After2020 |
By2020 |
By2018 |
By2020 |
By2020 |
By2020 |
By2020 |
By2020 |
By2014 |
By2020 |
By2018 |
By2020 |
By2018 |
By2020 |
By2018 |
By2014 |
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| 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 d...
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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 d...
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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 d...
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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 d...
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Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele zudem erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstel...
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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 d...
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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 d...
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Program is fully adequate
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See 5h answer
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See 5h answer.
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Please see section “Jūras monitoringa programmas nepilnību novēršanas plāns” in monitoring programme.
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Fill gaps in data and assessment methods.
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Filling the gaps in data and methods
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Filling of gaps in data and methods used.
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Filling the gaps in data and methods used.
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See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser
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See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
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See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
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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 von Belastungen und Aktivitäten, welche negative Einflüsse auf die Fischgemeinschaften ausüben, findet in den Monitoringprogrammen zu D2, D3, D5, D6, D7, D8, D10 und D11 statt.
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Bereits in der WRRL wurde ein Pressure-Bezug für benthische Indices nachgewiesen. Problematisch sind die Kausalbezüge in Systemen in denen mehrere Stressoren gleichzeitig wirken. Im Vergleich von Referenzgebieten (Stressorenausschluss) zu Belastungsgebieten wird der anstehende Test der Indikatoren /Parameter in Projekten zukünftig auch die Ableitung geeigneter Maßnahmen verbessern.
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Siehe Monitoringprogramm "Eutrophierung"
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Das Monitoring zu D3 bezieht sich auf die kommerzielle und nicht-kommerzielle (Freizeit-)Fischerei.
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DE nutzt zur Quantifizierung von Nährstoffemission aus punktuellen und diffusen Quellen in die Oberflächengewässer Deutschland routinemäßig Stoffeintragsmodelle (MONERIS, MoRe). Diese Modelle ermöglichen die Quantifizierung der unterschiedlichen Eintragspfade der Nährstoffemissionen (z.B. Grundwa...
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The programme provides data on key indicators in the marine area which together with relevant pressures impact the biodiveristy and the quality of the habitats at sea. |
The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures. |
The programme provides data on key indicators 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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Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
Hunting of sea-birds and Grey Seal is practiced in the whole coastal area. The hunting focuses on certain game species. Hunting of Grey Seal requires permit and a quota is set annually. The monitoring collects all game statistics. |
No monitoring of activities
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No monitoring activities
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Data collected from licensing authorities (eg. constructions, dredging) and automatic identification system (AIS) is used in an assessment of pressures by HELCOM in the Baltic Sea region. HELCOM cumulative impact assessments have identified the impacts of activities on marine environment. |
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. |
Siūloma žiemojančių jūros paukščių stebėsenos erdvinė apimtis, stebimų paukščių funkcinė ir rūšinė įvairovė bei stebėsenos periodiškumas leis laiku įvertinti pagrindines grėsmes ir poveikius, identifikuoti tokių poveikių mechanizmą ir laiku pasiūlyti atitinkamas poveikį švelninančias priemones, tuo pačiu užtikrinti GAB išlaikymą.
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The location of the sites will sufficiently cover the diversity of natural conditions in the area under assessment and the potential impact of human activities.
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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 programme combined with the information on the expand of human activity in the field of man made structures will proviede information on the impact on the descriptor. |
The programme will deliver data needed for the assessment pressures. |
The programme will give direct linkage to information on the pressere from fisheries as well as on the intensity of underwater noise. |
Pelagic habitats are reflecting human activity esspessially eutrofication and can be indicative on the changes in pressure output. |
Monitoring of ports performed once in 3 years will address frequency of occurrence of non indigenous species. It would enable the identification of possible measures. |
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats
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See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
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See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)
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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 | N |
N |
N |
N |
Y |
Y |
Y |
Y |
Y |
N |
Y |
Y |
Y |
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| Q7d - Established methods | Y |
Y |
N |
Y |
N |
N |
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| Q7d - Adequate understanding of GES | N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
N |
Y |
Y |
N |
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| Q7d - Adequate capacity | N |
Y |
N |
Y |
Y |
Y |
Y |
Y |
Y |
N |
Y |
Y |
Y |
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| Q7d - Addresses activities and pressures | N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
N |
Y |
Y |
Y |
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| Q7d - Addresses effectiveness of measures | N |
Y |
N |
N |
N |
N |
N |
N |
Y |
N |
Y |
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.
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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 Berichtsz...
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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.
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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.
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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 Berichtsz...
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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 Berichtsz...
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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 Berichtsz...
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A programme of measures is under preparation. Priority should be given to the effects and risks for which measures are needed. In the light of the proposed measures, it is envisaged to specify the objectives and related indicators and to assess the impact of the measures (individually for each me...
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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. |
The programme combined with the information on the expand of human activity in the field of man made structures will proviede information on the impact on the descriptor. |
The programme will deliver data needed for the assessment of progres with measures. |
Process not known
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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 |
After2020 |
By2018 |
After2020 |
By2020 |
By2020 |
By2020 |
By2014 |
By2020 |
By2020 |
By2020 |
By2014 |
By2020 |
By2014 |
By2020 |
By2014 |
By2014 |
By2018 |
By2014 |
By2018 |
By2014 |
By2018 |
By2014 |
By2014 |
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| Q8a - Links to existing Monitoring Programmes |
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| Reference sub-programme | Sub-programme ID | BALDE_Sub_105 |
BALDE_Sub_055 |
BALDE_Sub_056 |
BALDE_Sub_058 |
BALDE_Sub_061 |
BALDE_Sub_094 |
BALDE_Sub_095 |
BALDE_Sub_096 |
BALDE_Sub_125 |
BALDE_Sub_129 |
BALDE_Sub_087 |
BALDE_Sub_092 |
BALDE_Sub_083 |
BALDE_Sub_084 |
BALDE_Sub_087 |
BALDE_Sub_092 |
BALDE_Sub_097 |
BALDE_Sub_099 |
BALDK-D01-01_abundance_birds_breeding |
BALDK-D01-02_abundance_birds_wintering |
BALDK-D01-16_habitats_birds_wintering |
BALDK-D08-01_health_birds_breeding |
BALDK-D08-09_mortality_birds |
BALDK-D01-03_abundance_mammals_seals |
BALDK-D01-04_abundance_mammals_porpoise |
BALDK-D01-10_population_mammals_seals |
BALDK-D01-11_population_mammals_porpoise |
BALDK-D01-17_habitats_mammals_seals |
BALDK-D01-18_habitats_mammals_porpoise |
BALDK-D01-22_seabed_distribution |
BALDK-D06-02_abundance_hardbottom |
BALDK-D06-03_abundance_softbottomflora |
BALDK-D06-04_abundance_softbottomfauna |
BALDK-D06-06_physidisturb_trawl |
BALDK-D03-04_mortal_fisheries_birds |
BALDK-D03-05_mortal_fisheries_porpoise |
BALDK-D03-06_mortal_fisheries_seals |
BALDK-D03-08_mortal_fish_coastal |
BALDK-D03-10_mortal_fish_offsh_commercial |
BALDK-D05-01_micropath_water |
BALDK-D05-02_watercolumn_physical |
BALDK-D05-03_watercolumn_chemical |
BALDK-D05-04_planktonbloom |
BALDK-D05-05_NUTRI_input_land |
BALDK-D05-06_NUTRI_input_atmos |
BALDK-D08-01_health_birds_breeding |
BALDK-D08-02_health_fish_demersal |
BALDK-D08-03_health_fish_commercial |
BALDK-D08-06_health_fish_coastal |
BALDK-D08-09_mortality_birds |
BALDK-D08-10_health_hardbottomfauna |
BALDK-D08-12_health_softbottomfauna |
BALDK-D08-13_CONTAMIN_input_atmos |
BALDK-D08-14_CONTAMIN_INPUT_point_sources |
BALDK-D08-17_CONTAMIN_water |
BALDK-D08-18_CONTAMIN_sediment |
BALFI-D01,04,06bir-1 |
BALFI-D01,04,06bir-2 |
BALFI-D01,04,06bir-3 |
BALFI-D01,04,06bir-4 |
BALFI-D01,04,06fis-1 |
BALFI-D01,04,06fis-2 |
BALFI-D01,04,06fis-3 |
BALFI-D01,04,06mam-1 |
BALFI-D01,04,06mam-2 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-3 |
BALFI-D01,04,06ben-4 |
BALFI-D03-1 |
BALFI-D03-2 |
BALLT-D018_OiledBirds |
BALLT-D01_BirdsWinter |
BALLT-D01234_FishCoastal |
BALPL-D0104-WaterBirds |
BALPL-D0104-WhiteTailedEagle |
BALPL-D0104-Fish |
BALPL-D0104-Mammals |
BALPL-D0104-WaterColumnHabitats |
BALPL-D02-01_PortSurveys |
BALPL-D02-02_Fish |
BALPL-D02-03 |
BALSE-Birds-D14-Hackande |
BALSE-Birds-D14-Overvintrande |
BALSE-HAZ-D814-Havsorn |
BALSE-COMFISH-D314-Al |
BALSE-COMFISH-D314-Lax |
BALSE-Fish-D14-Kust |
BALSE-HAZ-D814-Fiskhalsa |
BALSE-HAZ-D814-Salhalsa |
BALSE-mammals-D14-Sal |
BALSE-mammals-D14-Tumlare |
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| Sub-programme name | Mobile species - abundance and/or biomass |
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) |
Mobile species - abundance and/or biomass |
Mobile species - health status |
Mobile species - population characteristics |
Other |
Benthic species - abundance and/or biomass |
Seabed habitats - community characteristics |
Seabed habitats - distribution and extent |
Seabed habitats - physical/chemical characteristics |
Other |
Other |
Pelagic habitats - community characteristics |
Plankton blooms (biomass, frequency) |
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) |
Nutrient inputs - from atmosphere |
Nutrient inputs - sea-based sources |
Pelagic habitats - community characteristics |
Plankton blooms (biomass, frequency) |
Water column - chemical characteristics |
Water column - physical characteristics |
Mobile species - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - state of habitats |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Mobile species - population characteristics |
Mobile species - state of habitats |
Mobile species - state of habitats |
Seabed habitats - community characteristics |
Physical disturbance - from dredging and disposal of dredged material |
Seabed habitats - physical/chemical characteristics |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Physical disturbance - from bottom trawling |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Microbial pathogen levels - in water column (bathing waters) |
Water column - physical characteristics |
Water column - chemical characteristics |
Plankton blooms (biomass, frequency) |
Nutrient inputs - land-based sources |
Nutrient inputs - from atmosphere |
Contaminant levels - in species, including seafood |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Benthic species - health status |
Benthic species - health status |
Contaminant inputs - from atmosphere |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from other human activities |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - health status |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Seabed habitats - distribution and extent |
Physical disturbance - from dredging and disposal of dredged material |
Activities extracting living resources (fisheries including recreational, maerl, seaweed) |
Activities extracting living resources (fisheries including recreational, maerl, seaweed) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - abundance and/or biomass |
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 |
Water column - physical characteristics |
Water column - chemical characteristics |
Nutrient levels - in water column |
Pelagic habitats - community characteristics |
Seabed habitats - physical/chemical characteristics |
Nutrient inputs - land-based sources |
Nutrient inputs - from atmosphere |
Plankton blooms (biomass, frequency) |
Mobile species - population characteristics |
Mobile species - population characteristics |
Mobile species - population characteristics |
Mobile species - population characteristics |
Pelagic habitats - community characteristics |
Non-indigenous species inputs - from specific sources |
Non-indigenous species - abundance and/or biomass |
Non-indigenous species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - health status |
Mobile species - health status |
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 |
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 |
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| Q4g - Sub-programmes | Sub-programme ID | BALDE_Sub_105 |
BALDE_Sub_055 |
BALDE_Sub_056 |
BALDE_Sub_058 |
BALDE_Sub_061 |
BALDE_Sub_094 |
BALDE_Sub_095 |
BALDE_Sub_096 |
BALDE_Sub_125 |
BALDE_Sub_129 |
BALDE_Sub_087 |
BALDE_Sub_092 |
BALDE_Sub_083 |
BALDE_Sub_084 |
BALDE_Sub_087 |
BALDE_Sub_092 |
BALDE_Sub_097 |
BALDE_Sub_099 |
BALDK-D01-01_abundance_birds_breeding |
BALDK-D01-02_abundance_birds_wintering |
BALDK-D01-16_habitats_birds_wintering |
BALDK-D08-01_health_birds_breeding |
BALDK-D08-09_mortality_birds |
BALDK-D01-03_abundance_mammals_seals |
BALDK-D01-04_abundance_mammals_porpoise |
BALDK-D01-10_population_mammals_seals |
BALDK-D01-11_population_mammals_porpoise |
BALDK-D01-17_habitats_mammals_seals |
BALDK-D01-18_habitats_mammals_porpoise |
BALDK-D01-22_seabed_distribution |
BALDK-D06-02_abundance_hardbottom |
BALDK-D06-03_abundance_softbottomflora |
BALDK-D06-04_abundance_softbottomfauna |
BALDK-D06-06_physidisturb_trawl |
BALDK-D03-04_mortal_fisheries_birds |
BALDK-D03-05_mortal_fisheries_porpoise |
BALDK-D03-06_mortal_fisheries_seals |
BALDK-D03-08_mortal_fish_coastal |
BALDK-D03-10_mortal_fish_offsh_commercial |
BALDK-D05-01_micropath_water |
BALDK-D05-02_watercolumn_physical |
BALDK-D05-03_watercolumn_chemical |
BALDK-D05-04_planktonbloom |
BALDK-D05-05_NUTRI_input_land |
BALDK-D05-06_NUTRI_input_atmos |
BALDK-D08-01_health_birds_breeding |
BALDK-D08-02_health_fish_demersal |
BALDK-D08-03_health_fish_commercial |
BALDK-D08-06_health_fish_coastal |
BALDK-D08-09_mortality_birds |
BALDK-D08-10_health_hardbottomfauna |
BALDK-D08-12_health_softbottomfauna |
BALDK-D08-13_CONTAMIN_input_atmos |
BALDK-D08-14_CONTAMIN_INPUT_point_sources |
BALDK-D08-17_CONTAMIN_water |
BALDK-D08-18_CONTAMIN_sediment |
BALFI-D01,04,06bir-1 |
BALFI-D01,04,06bir-2 |
BALFI-D01,04,06bir-3 |
BALFI-D01,04,06bir-4 |
BALFI-D01,04,06fis-1 |
BALFI-D01,04,06fis-2 |
BALFI-D01,04,06fis-3 |
BALFI-D01,04,06mam-1 |
BALFI-D01,04,06mam-2 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-3 |
BALFI-D01,04,06ben-4 |
BALFI-D03-1 |
BALFI-D03-2 |
BALLT-D018_OiledBirds |
BALLT-D01_BirdsWinter |
BALLT-D01234_FishCoastal |
BALPL-D0104-WaterBirds |
BALPL-D0104-WhiteTailedEagle |
BALPL-D0104-Fish |
BALPL-D0104-Mammals |
BALPL-D0104-WaterColumnHabitats |
BALPL-D02-01_PortSurveys |
BALPL-D02-02_Fish |
BALPL-D02-03 |
BALSE-Birds-D14-Hackande |
BALSE-Birds-D14-Overvintrande |
BALSE-HAZ-D814-Havsorn |
BALSE-COMFISH-D314-Al |
BALSE-COMFISH-D314-Lax |
BALSE-Fish-D14-Kust |
BALSE-HAZ-D814-Fiskhalsa |
BALSE-HAZ-D814-Salhalsa |
BALSE-mammals-D14-Sal |
BALSE-mammals-D14-Tumlare |
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| Sub-programme name | Mobile species - abundance and/or biomass |
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) |
Mobile species - abundance and/or biomass |
Mobile species - health status |
Mobile species - population characteristics |
Other |
Benthic species - abundance and/or biomass |
Seabed habitats - community characteristics |
Seabed habitats - distribution and extent |
Seabed habitats - physical/chemical characteristics |
Other |
Other |
Pelagic habitats - community characteristics |
Plankton blooms (biomass, frequency) |
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) |
Nutrient inputs - from atmosphere |
Nutrient inputs - sea-based sources |
Pelagic habitats - community characteristics |
Plankton blooms (biomass, frequency) |
Water column - chemical characteristics |
Water column - physical characteristics |
Mobile species - population characteristics |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - state of habitats |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - population characteristics |
Mobile species - population characteristics |
Mobile species - state of habitats |
Mobile species - state of habitats |
Seabed habitats - community characteristics |
Physical disturbance - from dredging and disposal of dredged material |
Seabed habitats - physical/chemical characteristics |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Physical disturbance - from bottom trawling |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Microbial pathogen levels - in water column (bathing waters) |
Water column - physical characteristics |
Water column - chemical characteristics |
Plankton blooms (biomass, frequency) |
Nutrient inputs - land-based sources |
Nutrient inputs - from atmosphere |
Contaminant levels - in species, including seafood |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Benthic species - health status |
Benthic species - health status |
Contaminant inputs - from atmosphere |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - mortality/injury rates from other human activities |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - health status |
Benthic species - abundance and/or biomass |
Benthic species - abundance and/or biomass |
Seabed habitats - distribution and extent |
Physical disturbance - from dredging and disposal of dredged material |
Activities extracting living resources (fisheries including recreational, maerl, seaweed) |
Activities extracting living resources (fisheries including recreational, maerl, seaweed) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - abundance and/or biomass |
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 |
Water column - physical characteristics |
Water column - chemical characteristics |
Nutrient levels - in water column |
Pelagic habitats - community characteristics |
Seabed habitats - physical/chemical characteristics |
Nutrient inputs - land-based sources |
Nutrient inputs - from atmosphere |
Plankton blooms (biomass, frequency) |
Mobile species - population characteristics |
Mobile species - population characteristics |
Mobile species - population characteristics |
Mobile species - population characteristics |
Pelagic habitats - community characteristics |
Non-indigenous species inputs - from specific sources |
Non-indigenous species - abundance and/or biomass |
Non-indigenous species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - abundance and/or biomass |
Mobile species - health status |
Mobile species - health status |
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 |
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 |
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| Q4l - Links of monitoring programmes of other Directives and Conventions |
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
In Deutschland werden die Monitoringanforderungen aller Meeres-relevanten EG-Richtlinien und internationalen Übereinkommen in einem gemeinsamen nationalen Messprogramm
(Bund-/Länder-Messprogramm) von den zuständigen Institutionen des Bundes und der Länder umgesetzt.
Die MSRL-Sub-Programme des...
|
NOVANA - http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
|
All these above activities are performed under the national Danish monitoring Program (NOVANA) as part of the national reporting to the Commission in relation to the Birds Directive. |
http://www.vildtsundhed.dk/english/Activities/Surveillance
|
http://www.vildtsundhed.dk/english/Activities/Surveillance
|
http://naturstyrelsen.dk/naturoplevelser/jagt/tilskadekommet-vildt/beredskabsplan-for-havpattedyr-og-havfugle/ http://naturstyrelsen.dk/media/nst/Attachments/Beredskabsplanforhavpattedyrmarts2012.pdf
There is established a contingency plan designed to ensure a coordinated and effective action on marine mammals and seabirds in an emergency or in case of strandings in the country.
An effective contingency plan is an important prerequisite for being able to take steps to mitigate or avert the effects of, for example, an oil disaster at sea or deaths of marine mammals.
The Danish contingency plan for marine mammals and seabirds have two main functions: 1) to build a knowledge base that makes it possible to prevent and 2) to monitor an evolving situation and take the necessary measures so that the sick, stranded and oil-contaminated animals do not suffer unnecessarily. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
There are no specific technical descriptions of the methods behing the distribution maps. It takes place in two phases - mapping of bottom substrates using either side scan sonar or multibeam sonar and surveys of the biological compositions of the areas using videosurveys. Definitions of the habitattypes follows a habitattype description written by the Danish Nature Agency in coorperation with DCE.
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/Biodiversitet/Habitat-beskrivelser-app4b-ver104_opdatering-havtyper2012.pdf. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.4 and figur 8.7 shows the position of the stations. 60% of the stations are in the BALDK area and 40% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ .
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.3 shows the position of the stations. 70% of the stations are in the BALDK area and 30% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.5 shows the position of the stations. 60% of the stations are in the BALDK area and 40% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive,Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
DTU Aqua has access to VMS data from all Danish commercial vessels from 2005 (above 15 meters) and from 2012 (above 12 meters). VMS data has been linked to logbook data and can therefore show pressure on the seabed by gear and target species.The access is to all Danish vessels within this size category in all waters. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
Catches from the recreational fisheries are registered on a voluntary basis by ”key” fishermen at fixed stations in most parts of the Danish coasts. The catches are performed with standard gillnets (one mesh size, 65 mm) and/or fyke nets, with up to 3 samples monthly in the beginning of each month, and from around April to November. Because of the mesh size used, the gillnets sample mostly adults, whereas juveniles of flounder and cod may be caught in the fyke nets. At present about 100+ fishers are invovled in the project. the last report with a detailed description can be downloaded:
http://orbit.dtu.dk/files/100552186/Publishers_version.pdf |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference.
A danish manual is avalible. |
Hereby link to the EU Bathing Water Directive (Directive 2006/7/EC of 15 February 2006):
http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:064:0037:0051:EN:PDF.
Please find also link to the Danish Statutory order concerning the bathing water quality: (BEK no. 939 of 18/09/2012)
https://www.retsinformation.dk/forms/R0710.aspx?id=143189. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.1 shows the position of the stations. 63% of the stations are in the BALDK area and 37% of the stations are in ANSDK area. Also se figur 8.9 that show addition station sampeled primæry during the season where hypoxia cann occur.
Technical manual for the marine survey:
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.1 shows the position of the stations. 63% of the stations are in the BALDK area and 37% of the stations are in ANSDK area. Also se figur 8.9 that show addition station sampeled primæry during the season where hypoxia cann occur.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.6 shows the position of the stations. 33% of the stations are in the BALDK area and 67% of the stations are in ANSDK area.
Technical manual for the marine survey:
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
'HELCOM
OSPAR
Danish "Action plan against nutrient pollution of the Danish Aquatic Environment" and subsequent national action plans.
Water Framework Directive |
The Danish monitoring program for air quality and atmospheric deposition contrubutes to the following other programmes: The EMEP monitoring program under CLRTAP, OSPAR, PARCOM and the monitoring in relation to the EU air quality directive (2008/50/EC). |
http://www.vildtsundhed.dk/english/Activities/Surveillance
|
The international coordinated trawl surveys are directed to the demersal species i.e. cod and flounder and other flatfishes in the Baltic Sea, however in the recent years other species are also intensively investigated to support ecosystem analyses. The survey is part of the Danish DCF covered under the CFP. |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible. |
NOVANA
OSPAR CEMP
HELCOM COMBINE
|
http://naturstyrelsen.dk/naturoplevelser/jagt/tilskadekommet-vildt/beredskabsplan-for-havpattedyr-og-havfugle/ http://naturstyrelsen.dk/media/nst/Attachments/Beredskabsplanforhavpattedyrmarts2012.pdf
There is established a contingency plan designed to ensure a coordinated and effective action on marine mammals and seabirds in an emergency or in case of strandings in the country.
An effective contingency plan is an important prerequisite for being able to take steps to mitigate or avert the effects of, for example, an oil disaster at sea or deaths of marine mammals.
The Danish contingency plan for marine mammals and seabirds have two main functions: 1) to build a knowledge base that makes it possible to prevent and 2) to monitor an evolving situation and take the necessary measures so that the sick, stranded and oil-contaminated animals do not suffer unnecessarily. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.3 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.10 and 8.11 shows the position of the stations. 50% of the stations are in the BALDK area and 50% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/vandmiljoe/overvaagning-af-vand-og-natur/
Table 8.3 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.10 and 8.11 shows the position of the stations. 50% of the stations are in the BALDK area and 50% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Seafood Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
The Danish monitoring program for air quality and atmospheric deposition contrubutes to the following other programmes: The EMEP monitoring program under CLRTAP, OSPAR, PARCOM and the monitoring in relation to the EU air quality directive (2008/50/EC). |
Water framework directive
IPPC-directive
COUNCIL DIRECTIVE of 4 May 1976 on pollution caused by certain dangerous substances discharged into the aquatic environment of the Community (76/464/EEC)
OSPAR
HELCOM
Stockholmkonvention
The strategy in the monitoring programme is meeting of all obligations and needs within the same programme if possible. |
NOVA national monitoring program, Bay of Aarhus.
|
NOVANA
OSPAR CEMP
HELCOM COMBINE
|
This sub-programme refers to the monitoring which has been reported under the Birds Directive and the Habitats Directive.
Further information describing this national sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/
Monitoring of marine breeding birds is not yet fully coordinated at region level. |
HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution
Essential information describing this national sub-programme is available in the above mentioned HELCOM Monitoring manual sub-programme. |
Not relevant
|
Essential information describing this national sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
Not relevant
|
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: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance |
Essential information describing this national sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status |
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna
HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics
Essential information describing this national sub-programme is available in the above mentioned HELCOM Monitoring manual sub-programme. |
This sub-programme also refers to the monitoring which has been reported under the Water Framework Directive (Benthic fauna).
Further information describing this national sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna
HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics |
This sub-programme refers to the monitoring which has been reported under the Water Framework Directive (Benthic fauna).
Further information describing this national sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species .
HELCOM Monitoring manual - Sub-programme: Habitat forming species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/habitat-forming-species-and-substrates |
This sub-programme refers to the monitoring which has been reported under the Water Framework Directive. |
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 |
Birds directive. Monitoring will be incorporated in wintering birds monitoring programme and described in text-based paper report, 11-13 pages. |
Habitats directive, Birds directive. Monitoring described in the programme (paper report,7-11 pages) |
Water Framework directive, Habitats directive; Monitoring incorporated into present programme and described in Monitoring programme description, paper report. |
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 |
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 |
Monitoring of offshore fish species is performed in frame of BITS surveys within ICES. |
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 |
Programme is performed as a Helcom Combine Monitoring and reflects all relevant criteria and indicators for MSFD. |
http://www.helcom.fi/Lists/Publications/Non-native%20species%20survey%20protocols,%20target%20species%20selection%20and%20risk%20assessment%20tools%20for%20the%20Baltic%20Sea%20HELCOM%20ALIENS%202.pdf#search=alien%20species%20port%20surveys |
http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf
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http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf
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"Sub-programme Marine breeding birds abundance in HELCOM Monitoring Manual
Data from the sub-programme contribute to:
Birds Directive
African European Waterfowl Agreement (AEWA) and the Ramsar convention. |
Sub-programme Marine wintering birds abundance in HELCOM Monitoring Manual
Data from the sub-programme contribute to:
Birds Directive
Habitats Directive
African European Waterfowl Agreement (AEWA) and the Ramsar convention.
The monitoring of wintering seabirds are part of the international seabird surveys which are coordinated by Wetlands International. |
Sub-programme Marine bird health in HELCOM Monitoring Manual |
Monitoring is part of the Common Fisheries Policy - Data Collection Framework
Helcom monitoring manual - sub-programme Migratory fish |
Monitoring is part of the Common Fisheries Policy - Data Collection Framework
Helcom monitoring manual - sub-programme Migratory fish |
WFD monitoring
Monitoring for the Habitats directive
CFP
HELCOM Monitoring Manual - sub-programme Costal fish |
"HELCOM COMBINE supporting programme
http://helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual" |
Sub-programme Health status in HELCOM Monitoring Manual |
Habitats Directive
Helcom monitoring manual - Sub-programme Seal abundance |
Habitats Directive
Helcom monitoring manual - Sub-programme 3: Harbour porpoise abundance |
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| Q5c - Features | Q5c - Habitats |
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| Q5c - Species list |
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| Q5c - Physical/Chemical features |
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| 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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| Species population size |
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| Species population characteristics |
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| Species impacts |
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| Habitat distribution |
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| Habitat extent |
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| Habitat condition (biological) |
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| Habitat impacts |
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| Q9b - Parameters monitored (pressures) | Pressure input |
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| Pressure output |
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| Q9b - Parameters monitored (activity) | Activity |
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| Q9b Parameters monitored (other) | Other |
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| Q41 Spatial scope | EEZ TerritorialWaters |
EEZ TerritorialWaters |
EEZ TerritorialWaters |
EEZ TerritorialWaters |
EEZ TerritorialWaters WFD_CW |
EEZ TerritorialWaters WFD_CW |
TerritorialWaters WFD_CW EEZ |
TerritorialWaters WFD_CW EEZ |
EEZ TerritorialWaters WFD_CW |
EEZ TerritorialWaters WFD_CW |
EEZ TerritorialWaters WFD_CW |
EEZ TerritorialWaters WFD_CW |
MSland_FW EEZ TerritorialWaters WFD_CW |
MSland_FW |
EEZ TerritorialWaters WFD_CW |
EEZ TerritorialWaters WFD_CW |
EEZ TerritorialWaters WFD_CW |
EEZ TerritorialWaters WFD_CW CS BeyondMSwaters |
MSland_FW |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW WFD_CW |
MSland_FW |
WFD_CW TerritorialWaters EEZ |
MSland_FW |
WFD_TW WFD_CW TerritorialWaters |
MSland_FW |
WFD_CW TerritorialWaters |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
WFD_CW |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW |
WFD_CW EEZ BeyondMSwaters |
WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
MSland_FW |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW |
MSland_FW WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW |
WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_CW |
WFD_CW TerritorialWaters |
WFD_CW TerritorialWaters |
WFD_CW TerritorialWaters |
WFD_CW |
WFD_TW |
WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
TerritorialWaters BeyondMSwaters |
WFD_CW TerritorialWaters |
WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_TW WFD_CW |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_TW |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_TW WFD_CW TerritorialWaters EEZ |
WFD_CW |
WFD_CW |
WFD_CW |
WFD_CW |
WFD_CW |
WFD_CW |
WFD_CW |
WFD_CW |
WFD_CW |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
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| Q4j - Description of spatial scope |
Kompletterfassung, Erfassung in Schutzgebieten
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Kompletterfassung, Erfassung in Schutzgebieten
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Tiere des Monitorings entstammen diesen Gebieten
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Kompletterfassung, Erfassung in Schutzgebieten
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Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO (Bund/Länder-Messprogramm / Bund/Länder-Ausschuss Nord- und Ostsee)
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Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO (Bund/Länder-Messprogramm / Bund/Länder-Ausschuss Nord- und Ostsee)
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Entspricht der Zuständigkeit des Landes Schleswig Holstein
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Entspricht der Zuständigkeit des Landes Schleswig Holstein
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Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO (Bund/Länder-Messprogramm / Bund/Länder-Ausschuss Nord- und Ostsee)
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Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO (Bund/Länder-Messprogramm / Bund/Länder-Ausschuss Nord- und Ostsee)
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keine Angabe vorhanden!!
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Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO (Bund/Länder-Messprogramm / Bund/Länder-Ausschuss Nord- und Ostsee)
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Emissionsquellen befinden sich an Land EMEP erstellt jährlich Daten und Karten der Stickstoff-Deposition für die gesamte Nord- und Ostsee mit einer Auflösung von 0,1° x 0,1°Long/Lat.
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gemessen werden die Nährstoffkonzentrationen und der Abfluss am Übergabepunkt limnisch-marin der in die Ostsee mündenden Flüsse
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keine Angabe vorhanden!!
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Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO (Bund/Länder-Messprogramm / Bund/Länder-Ausschuss Nord- und Ostsee)
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Verpflichtungen insbesondere nach WRRL, MSRL, HELCOM, BLMP/BLANO Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO ("Bund/Länder-Messprogramm" / "Bund/Länder-Ausschuss Nord- und Ostsee")
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Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO ("Bund/Länder-Messprogramm" / "Bund/Länder-Ausschuss Nord- und Ostsee") Erfassung der AWZ von Nord- und Ostsee, um den physikalischen Zustand und Ursachen potentieller Veränderungen bewerten zu können. Die Messregion wird durch 2 Faktoren besti...
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For the species Sandwich Tern, Arctic Tern, Common Tern and Little Tern under the programme NOVANA:
Start date: 01-05-2006
End Date: 9999
For Great Cormorant:
Start date: 01-05-1993
End Date: 9999.
No programme for any other of the marine birds that breed in Denmark, e.g. Common Guillemot, Razorbill, Black Guillemot, Common Eider, gulls, mergansers.
In principle should all potential breeding sites of the four tern species be monitored by NOVANA, but the experience is that probably around 50-70 % of the relevant sites have been monitored by the NOVANA programme. Consequently, temporal development can be tracked for some but not all sites. |
All these above activities are performed under the national Danish monitoring Program (NOVANA) as part of the national reporting to the Commission in relation to the Birds Directive. |
Monitoring is performed under the National Monitoring Programme for Water and Nature, NOVANA in order to implement the monitoring requirements of the Natura2000 directives. |
Wildlifehealth.dk survey the health status of the Danish wildlife continuously. The surveillance consist of both active and passive (necropsy of dead game submitted to Wildlifehealth.dk) and active (sampled on purpose to establish the health status of the species in a region) surveillance. Information from both surveillance programmes are used for research. |
All coastal areas
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Harbour seals monitored since 1979.
Grey seals monitored since 2011.
All sites where seals go on land are included in the program. |
Harbour porpoises occur in all Danish waters. Every 5-6th year an international survey (mini-SCANS+SCANS) conduct an abundacea survey covering this region except for Bornholm waters. For Bornholm waters a new method using acoustic data loggers have been developed (SAMBAH), but is not yet part of the national monitoring program. |
In Danish waters there is 4 populations of harbour seals and 2 populations of grey seals. In this region both the Kattegat and western Baltic harbour seal population is shared with Sweden. The Baltic grey seal population is shared with Sweden, Finland and Estonia. |
Denmark share 3 harbour porpoise poulations with the North Sea ranage states (North Sea population), Sweden and Germany (Belt Sea population) and the Baltic proper range states (Baltic population). The Baltic Sea poulation and half of the Belt Sea population is living within the BALDK region |
Harbour seals monitored since 1979.
Grey seals monitored since 2011.
All land sites are monitored but there is no program covering the marine part of the seals's habitat. |
All major Natura2000 sites within this region is monitored. |
The monitoring is not systematic. Larger scale distribution mapping of reefs and sandbanks started in 2011.
Mapping takes place within Natura 2000 areas and specific mapping of deep muddy bottom and shallow mud surfaces are not mapped. |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions. |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions. |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions. |
The vessel monitoring system (VMS) is a satellite-based monitoring system which at regular intervals provides data to the fisheries authorities on the location, course and speed of vessels. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
The aim of the "Key-fishermen" projects is to register fish catches and document fish assemblages in Danish coastal waters over a consecutive number of years. |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
This program includes the entire coastline, inland waters (estuaries) and lakes. |
The program including rationale for the geographic scope can be found here;
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
The aim of the National Monitoring Programme for Water and NAture is to document the impacts of the current Programmes of Measures as well as to establish the basis for future environmental management of the Danish sea territories. |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ |
The programme has been established in order to document trends and inputs impacting the aquatic environment as well as to provide a basis for decision-making in relation to restore the environmental quality in freshwater and marine environment. |
The Danish monitoring program for air quality and depositons is based on a few coastal fixed measurements stations in combination with modelcalculations that cover all the Danish marins waters. The quality of the model calculations is based on comparisons with the results from the monitoring stations. |
Wildlifehealth.dk survey the health status of the Danish wildlife continuously. The surveillance consist of both active and passive (necropsy of dead game submitted to Wildlifehealth.dk) and active (sampled on purpose to establish the health status of the species in a region) surveillance. Information from both surveillance programmes are used for research. |
BITS is an international ICES coordinated survey, were Denmark gets appointed stations in Danish EZ zone as well as in international water in the Baltic. For every survey conducted a new list of stations is appointed and the area covered can vary between surveys. However, as a standard Denmark is conducting 18*2 days survey each year and this corresponds to 50 fishing stations and 80 plankton stations in the 1st quarter and similar in the 4th quarter survey. An international ICES manual is followed and a link to the newest version is added. DTU Aqua is participating in the ICES group (WGBIFS) coordinating the survey.
http://www.ices.dk/marine-data/Documents/DATRAS%20Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
In representative coastal areas, coordinated with the monitoring activities on contaminnant levels in fish. |
All coastal areas
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The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/vandmiljoe/overvaagning-af-vand-og-natur/
The monitoring program is developed for both the Water Framework directive and adapted and expanded for the Habitats directive. It monitors development, species composition and biodiversity on reefs at different depths. It therefore contributes to the monitoring of impacts of measures as well as establishes the basis for future environmental managerial decisions. |
The Danish monitoring program for air quality and depositons is based on a few coastal fixed measurements stations where concentrations in air and wetdeposition is measured. The results from these measurements is in a simple way extrapolateed to cover the Danish land areas and the inner Danish waters. For organic cantaminants only measurents of wet deposition a to measurements sites is carried out. |
The programme is set up in order to cover the whole country and therefore also for the reporting area. Descibed in chap. 3 in the description of the programme: http://naturstyrelsen.dk/media/nst/Attachments/NOVANA_2del.pdf |
Transect from harbour.
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Danish parts of HELCOM convention.
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HELCOM Monitoring manual - Sub-programme: Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/
Currently the whole counting network consists of 43 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year. |
HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution |
Mass mortalities of breeding sea birds are monitored in the vicinity of breeding colonies. Therefore the monitoring is focuses on islands and islets in coastal and territorial waters. |
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
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: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance |
HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status |
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
HELCOM Monitoring manual - Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species .
HELCOM Monitoring manual - Sub-programme: Habitat forming species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/habitat-forming-species-and-substrates |
Siltation, dredging and selective exploitation of seabed is carried out in the coastal areas of all Finnish marine sub-basins. |
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 |
Birds are monitored in coastal areas (beaches).
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Monitoring is carried out along the coast in every 3 years. Monitoring will be expanded to territorial and Exclusive Economic Zone (information in paper report 7-11 pages) with the frequency one time per 2 years. |
Monitoring is carried out in accordance to the HELCOM methods, described in Monitoring programme description, paper report, 16-17 pages |
The programme is designed to reflect state of higle mobile species which occure in the whole Polish EEZ of the Baltic Sea. |
The programme is designed to reflect state of higle mobile species which occure in the whole Polish EEZ of the Baltic Sea. |
The programme is designed to reflect state of higle mobile species which occure in the whole Polish EEZ of the Baltic Sea. |
The pilot programme aims to reflect state of higle mobile species which occure in the whole Polish EEZ of the Baltic Sea. |
The programme is designed to reflect the state of water column habitats and is following recommendations of the HELCOM monitoring guidelines. |
The programme will cover all major ports in Poland. |
The data for the programme will be available from Fish Monitoring programme. |
The data for the programme will be available from HELCOM Monitoring programme. |
See sub-programme Häckande sjöfågel, chapter Rumslig och tidsmässig täckning
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See sub-programme Övervintrande sjöfågel, chapter Rumslig och tidsmässig täckning
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See sub-programme Reproduktion hos havsörn, chapter Rumslig och tidssmässig täckning
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See sub-programme Migrerande fiskarter - ål, chapter Rumslig och tidsmässig täckning
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See sub-programme Migrerande fiskarter - lax, chapter Rumslig och tidsmässig täckning
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See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning
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See sub-programme Hälsotillstånd hos kustfisk, chapter Rumslig och tidsmässig täckning
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Se sub-programme Hälsotillstånd hos säl, chapter Rumslig och tidsmässig täckning
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See sub-programme Bestånd av säl, chapter Rumslig och tidsmässig täckning
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See sub-programme Bestånd av tumlare, chapter Rumslig och tidsmässig täckning
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| Q4h - Temporal scope | Start date- End date | 2008-9999 |
- |
2008-9999 |
1991-9999 |
2008-9999 |
- |
2006-9999 |
2006-9999 |
2012-9999 |
2012-9999 |
2006-9999 |
2006-9999 |
1979-9999 |
1979-9999 |
- |
1990-9999 |
1994-9999 |
1979-9999 |
1979-9999 |
1980-9999 |
2010-9999 |
- |
1993-9999 |
2000-9999 |
1932-9999 |
1932-9999 |
1991-9999 |
1979-9999 |
2011-9999 |
1979-9999 |
2011-9999 |
1979-9999 |
2011-9999 |
- |
2011-9999 |
1990-9999 |
1987-9999 |
1990-9999 |
2005-9999 |
1995-9999 |
1995-9999 |
1995-9999 |
2005-9999 |
1995-9999 |
1975-9999 |
1987-9999 |
1987-9999 |
1987-9999 |
1989-9999 |
1989-9999 |
- |
1932-9999 |
1991-9999 |
1995-9999 |
2004-9999 |
1991-9999 |
1998-9999 |
1998-9999 |
1989-9999 |
1998-9999 |
2001-2003 |
1998-9999 |
1948-9999 |
1965-9999 |
1986-9999 |
1970-9999 |
1980-9999 |
1976-9999 |
1970-9999 |
1988-9999 |
1977-9999 |
1965-9999 |
1965-9999 |
2006-9999 |
2014-9999 |
1970-9999 |
1970-9999 |
1992-2003 |
1998-9999 |
1992-9999 |
- |
- |
2011-9999 |
2015-9999 |
2014-9999 |
2016-2018 |
1999-9999 |
2016-2019 |
2014-9999 |
2014-9999 |
2010-9999 |
1967-9999 |
1965-9999 |
2004-9999 |
2004-9999 |
1960-9999 |
1988-9999 |
1977-9999 |
1975-9999 |
2011-9999 |
- |
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| Q9h - Temporal resolution of sampling |
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| Q9c - Monitoring method | || MP_130 || BLMP-online Kennblatt "Vögel" http://fino.bsh.de/blmpweb/kennblatt?id=8&kapitel=3&html=on |
|| MP_132 || BLMP-online Kennblatt "Säuger" http://fino.bsh.de/blmpweb/kennblatt?id=9&kapitel=3&html=on |
|| MP_131 || BLMP-online Kennblatt "Säuger" http://fino.bsh.de/blmpweb/kennblatt?id=9&kapitel=3& |
|| MP_132 || BLMP-online Kennblatt "Säuger" http://fino.bsh.de/blmpweb/kennblatt?id=9&kapitel=3&html=on |
|| MP_056, MP_118, MP_119, MP_129 || |
|| MP_119 || |
|| MP_031, MP_135 || |
|| MP_031, MP_134, MP_135 || |
|| MP_118 || |
|| MP_056 || |
|| MP_037 || HELCOM COMBINE manual http://www.helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual || MP_041 || BLMP (2009) Prüfverfahren-SOP http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM.pdf |
|| MP_039 || HELCOM COMBINE manual http://www.helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual |
|| MP_108 || EMEP: Centre of Emission Inventories and Projections (CEIP) http://www.ceip.at/ms/ceip_home1/ceip_home/reporting_instructions/ || MP_109 || EMEP-Modellierung: Meteorological Synthesizing Centre West of EMEP (MSC-W) http://emep.int/mscw/index_mscw.html
EMEP-Messungen: Chemical Coordinating Centre of EMEP (CCC) http://www.nilu.no/projects/ccc/index.html
HELCOM http://helcom.fi/Recommendations/Rec%2024-1.pdf |
|| MP_044 || HELCOM PLC Guidelines http://www.helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/plc-water-guidelines/ |
|| MP_037 || HELCOM COMBINE manual http://www.helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual || MP_041 || BLMP (2009) Prüfverfahren-SOP http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM.pdf |
|| MP_039 || HELCOM COMBINE manual http://www.helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual |
|| MP_021 || MHB-Kennblatt Hydrochemie http://fino.bsh.de/blmpweb/kennblatt?id=25&kapitel=3&html=on#Hydrochemie_32
Kranzwasserschöpfer – s. HELCOM COMBINE Manual, Annex C-2, p. 216 ff http://helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM.pdf || MP_033 || HELCOM COMBINE Manual, Annex B-8 http://www.helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual |
|| MP_035 || HELCOM COMBINE Manual, Annex C-2 http://helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM.pdf || MP_107, MP_110, MP_127 || |
For the species Sandwich Tern, Arctic Tern, Common Tern, Little Tern under the programme NOVANA (a technical description of the method exists):
The number of breeding pairs is estimated by counting the number of adults present in the colony/area of the colony and multiply this with 0.7.
This is the standard method used in the International Wadden Sea.
For Great Cormorant all occupied nests are counted at the time of season when the numbers of occupied nests are expected to be at their highest.
The person collating and writing up the data will check whether numbers reported seem reasonable and in some cases request details from the person that collected the data.
National standard: One person collates all information reported. Some of it is written up and published regularly. |
http://www.ens.dk/sites/ens.dk/files/undergrund-forsyning/vedvarende-energi/Abundance%20and%20distribution%20of%20selected%20waterbird%20species%20in%20Danish%20marine%20areas.pdf
http://www2.dmu.dk/Pub/ar261.pdf
http://www2.dmu.dk/Pub/FR606.pdf |
Passive disease surveillance in collaboration between The Danish Nature Agency and The National Veterinary Institute. |
Passive disease surveillance in collaboration between The Danish Nature Agency and The National Veterinary Institute. |
In case ofan oil spill where oiled birds are registered, the total number will be estimated and species registered. Samples of wings will be collected for age estimate http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf |
The national monitoring program (NOVANA) is described (in Danish) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M16_Artsovervaagning_af_saeler.pdf |
The national monitoring program (NOVANA) is described (in Danish) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M15_Artsovervaagning_af_marsvin.pdf |
The national monitoring program (NOVANA) is described (in Dansih) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M16_Artsovervaagning_af_saeler.pdf |
The national monitoring program (NOVANA) is described (in Danish) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M15_Artsovervaagning_af_marsvin.pdf |
The national monitoring program (NOVANA) is described (in Dansih) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M16_Artsovervaagning_af_saeler.pdf |
The national monitoring program (NOVANA) is described (in Dansih) at: http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M15_Artsovervaagning_af_marsvin.pdf |
Methods are described in the mapping reports such as the 2011 report which can be found here: http://www2.nst.dk/Download/Udgivelser/N2000_Marin_raastof_naturtypekort_kattegat_oestersoe_2011.pdf |
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del4/TA04_4_2_Haardbundsfauna.pdf |
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M12_Makroalger_paa_kystnaer_haard_bund__VERSION_2_.pdf |
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del4/TA04_4_1_Bloedbundsfauna.pdf |
http://icesjms.oxfordjournals.org/content/68/1/245.abstract |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
In this project 102 voluntary recreational fishermen participated, using either gillnets, fyke-nets or both gear types. Note that the results resented in this report represent catches reported by recreational fishermen. All species have caught have been registered and length measurements have been taken. The results showed a high fish biodiversity in Danish coastal waters. A total of 49 fish species were registered in gillnets and 72 in fyke-nets. This projec represent the largest and longest time series on catches in gillnets and fyke-nets along the Danish coasts. As age and length and weight by age are followed on a regular basis it is possible to follow the development over time, to estimate if the population is in a healthy state. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
Description of the technical method is described in the Bathing Water Directive 2006/7/EC of 15 February 2006 Article 15 and must be in accordance with Annex I, IV and V in this Directive. Link enclosed:
http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:064:0037:0051:EN:PDF.
Please find also a technical description of the method described in the Danish Statutory order (Statutory Order No. 2012-09-18. 939) concerning bathing and swimming areas. Reference to chapter 2 § 4/2. Link enclosed:
https://www.retsinformation.dk/forms/R0710.aspx?id=143189.
Attached is also a general technical description of measurement methods in the Danish Statutory Order (Statutory Order No. 231 of 05/03/2014) concerning quality standards for environmental measurements:
https://www.retsinformation.dk/Forms/R0710.aspx?id=160496 |
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M03_CTD_maaling__VERSION_2_.pdf
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M04_Ilt_i_vandsoejlen.pdf
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M05_Fluorescens_ver1.pdf
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M06_Lyssvaekkelse_ver1.pdf |
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_2_vandkemi.pdf |
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_5_fytoplankton.pdf |
References: Technical guideline documents for NOVANA is available from the Danish Nature Agency (in Danish), .and Bekendtgørelse om kvalitetskrav til miljømålinger (Statutory Order on Quality requirements in environmental analyses) https://www.retsinformation.dk/Forms/R0710.aspx?id=160496 |
The measurement methods are based on the methods recommended under the EMEP monitoring program. Part of the measurement methods has been slghtly modified compared to the EMPE methods. The modifications have been documented in connection with DCE's accriditation. The model calculations is based on DCE's air quality model called Danish hemispheric eulerian model. |
Passive disease surveillance in collaboration between The Danish Nature Agency and The National Veterinary Institute. |
ICES methods. Dioxin samples are analysed and published from DTU food. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. Other parameter measured in connection to health is condition to commarcial species. This is monitored over time to detect changes in health and growth. Furthermore, all herring aged are also analysed for the parasite nematode Anasaki in the laboratory. |
Method according to The Marine Topic Centre (M-FDC) technical guidelines (in Danish): TA M26 Biologisk effektmonitering i fisk
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M26_Biologisk_effektmonitering_i_fisk__ver_1_.pdf |
In case ofan oil spill where oiled birds are registered, the total number will be estimated and species registered. Samples of wings will be collected for age estimate http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf |
"1) OSPAR JAMP guideline on contaminant specific effects, Tecnical annex 3 on TBT-specific effects.
2) ICES TIMES guideline on lysosomal membrane stability. Both guidelines are incoorprated into the national monitoring guideline on either TBT-specific effects in marine snails and biological effects in mussels" |
"1) OSPAR JAMP guideline on contaminant specific effects, Tecnical annex 3 on TBT-specific effects
2) ICES TIMES guideline on lysosomal membrane stability. Both guidelines are incoorprated into the national monitoring guideline on either TBT-specific effects in marine snails and biological effects in mussels" |
The measurement methods are based on the methods recommended under the EMEP monitoring program. |
The samples are collected according to national technical instructions. Link to the technical instructions on sampling in the monitoring programme on point sources: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ta-for-punktkilder/. Demands for sample handling are given in special specification, which are provided by the Reference Laboratory/the Danish Nature Agency. Link to method specifikations: http://www.reference-lab.dk/metodedatablade/metodedatablade-kemiske.aspx. Demands for the analyses are found in legislation: Bekendtgørelsen om kvalitetskrav til miljømålinger nr 231 af 5. marts 2014 https://www.retsinformation.dk/Forms/R0710.aspx?id=160496. |
NOVA monitoring guidelines for NOVA 1998-2005 program.
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_8_MFS_havvand.pdf |
HELCOM (2014). Manual for marine Monitoring in the COMBINE programme of HELCOM.
http://helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual incorporated into technical annexes for the national NOVANA program |
HELCOM Monitoring manual - Sub-programme: Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/
Currently the whole counting network consists of 43 selected breeding areas situated along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year. |
HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution |
The frequency of mortality events and the number of dead seabird species are recorded |
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
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: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance |
HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status |
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna
HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics
Essential information describing this national sub-programme is available in the above mentioned HELCOM Monitoring manual sub-programme. |
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna
HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics
Essential information describing this national sub-programme is available in the above mentioned HELCOM Monitoring manual sub-programme. |
HELCOM Monitoring manual - Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species .
HELCOM Monitoring manual - Sub-programme: Habitat forming species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/habitat-forming-species-and-substrates
HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/stc/files/CombineManual/PartC/AnnexC9.pdf |
The level of contaminants (Hg, Cd, Cu, PAH, PCB, TBT) and the volume of dredged masses are measured as a part of monitoring of licensed activities along the Finnish coast. The volume of dredged masses are measured and the contaminant levels are determined by standard methods.The cumulative effects of selective exploitation of the seabed is also monitored within this sub-programme. Information on marine constructions and shipping is collected through licensing authorities and HELCOM. |
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 |
Method described in Monitoring programme, text-based paper report. |
Monitoring described in the programme (paper report,7-11 pages) |
Method described in Monitoring programme, text-based paper report. |
Meissner W., Bzoma Sz., 2013. Monitoring ptaków w tym monitoring obszarów specjalnej ochrony ptaków Natura 2000, faza IV, lata 2012-2015, Ogólnopolskie Towarzystwo Ochrony Ptaków na zlecenie GIOŚ, sfinansowane ze środków NFOŚiGW, maj 2013
and
Cenian Z., Chodkiewicz T., 2013. Monitoring Ptaków, Część E. Monitoring Ptaków Drapieżnych, online: http://www.monitoringptakow.gios.gov.pl/48.monitoring ptakow_drapieznych_mpd.html |
Meissner W., Bzoma Sz., 2013. Monitoring ptaków w tym monitoring obszarów specjalnej ochrony ptaków Natura 2000, faza IV, lata 2012-2015, Ogólnopolskie Towarzystwo Ochrony Ptaków na zlecenie GIOŚ, sfinansowane ze środków NFOŚiGW, maj 2013
and
Cenian Z., Chodkiewicz T., 2013. Monitoring Ptaków, Część E. Monitoring Ptaków Drapieżnych, online: http://www.monitoringptakow.gios.gov.pl/48.monitoring ptakow_drapieznych_mpd.html |
For offshore fish the BITS method is applied:
https://datras.ices.dk/Documents/Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf
For coastal fish national method http://www.gios.gov.pl/images/dokumenty/pms/monitoring_wod/przewodnik_metodyczny_20150420.pdf based on HELCOM http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Guidelines%20for%20Coastal%20fish%20Monitoring%20of%20HELCOM.pdf is applied |
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://www.helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual |
http://www.helcom.fi/Lists/Publications/Non-native%20species%20survey%20protocols,%20target%20species%20selection%20and%20risk%20assessment%20tools%20for%20the%20Baltic%20Sea%20HELCOM%20ALIENS%202.pdf#search=alien%20species%20port%20surveys |
http://www.gios.gov.pl/images/dokumenty/pms/monitoring_wod/przewodnik_metodyczny_20150420.pdf based on
http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Guidelines%20for%20Coastal%20fish%20Monitoring%20of%20HELCOM.pdf |
http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf |
"Censuses of breeding seabirds in the Bothnian Bay
http://www.lansstyrelsen.se/vasterbotten/SiteCollectionDocuments/Sv/Publikationer/2010/Samordnad%20%C3%B6vervakning%20kustf%C3%A5gel%20BV.pdf |
Standardized censuses of wintering birds, in accordance with IWC methods. Censuses of birds - individual counts of staging and wintering seabirds - BIN 16.1 and BIN 16.3, Naturvårdsverket 1978 http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/BIN_F_16_sjofagel.pdf |
"Undersökningstyp Havsörn, bestånd
http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/Undersokningstyper/kust%20och%20hav/havsorn.pdf" |
Test fishing is carried out according to methods under revison and descriptions of methods will be avalible on the web in the future. |
Test fishing is carried out according to methods under revison and descriptions of methods will be avalible on the web in the future. |
Test fishing with nets according to the Swedish monitoring method described in "Provfiske i Östersjöns kustområden- Djupstratifierat provfiske med Nordiska kustöversiktsnät". https://www.havochvatten.se/download/18.64f5b3211343cffddb280005491/1348912813575/undersokstyp-provfiske-ostersjon-kustomraden-djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.pdf |
"Undersökningstyp Hälsotillstånd hos kustfisk – biologiska effekter på subcellulär och cellulär nivå
http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/Undersokningstyper/kust%20och%20hav/fiskhalso.pdf" |
"Undersökningstyp Patologi hos gråsäl, vikaresäl och knubbsäl
http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/Undersokningstyper/kust%20och%20hav/salpatologi.pdf" |
Bestånd av knubbsäl och
vikaresäl
https://www.havochvatten.se/download/18.64f5b3211343cffddb280003193/1348912813047/Metodbeskrivning+Best%C3%A5nd+av+knubbs%C3%A4l+och+vikares%C3%A4l.pdf
Gråsälbestånd
https://www.havochvatten.se/download/18.64f5b3211343cffddb280003206/1348912813096/Metodbeskrivning+Gr%C3%A5s%C3%A4lsbest%C3%A5nd.pdf
"Gråsälsbestånd" will soon be replaced by an updated version at the following webpage:
https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/miljoovervakningens-metoder-och-undersokningstyper-inom-programomrade-kust-och-hav.html |
The SAMBAH surveys; Acoustic monitoring.
http://www.sambah.org/Methods.htm |
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| Q9d - Description of alteration to method | || MP_130 || |
|| MP_132 || Methoden-Standards BLMP (QS-Stelle UBA) in Entwicklung |
|| MP_131 || |
|| MP_132 || Methoden-Standards BLMP (QS-Stelle UBA) in Entwicklung |
|| MP_056, MP_129 || Tiefengrenzen, Dichte, Biomasse, Artenzahl || MP_118 || durch Taucher oder per UV-Video || MP_119 || Per Greifer oder Stechkasten werden Sedimentproben genommen und deren Fauna > 1mm herausgesiebt und bestimmt, Dredge |
|| MP_119 || Per Greifer oder Stechkasten werden Sedimentproben genommen und deren Fauna > 1mm herausgesiebt und bestimmt, Dredge |
|| MP_031 || Hydroakustische Messungen (Sidescan Sonar und Sediment- und Fächerecholot), ergänzt durch Greiferproben und Unterwasservideo || MP_135 || Seitensichtsonar, hochauflösendes Sedimentlot, Greiferproben mit anschließender Bestimmung der Korngrößenverteilung und Unterwasservideo |
|| MP_031 || Hydroakustische Messungen (Sidescan Sonar und Sediment- und Fächerecholot), ergänzt durch Greiferproben und Unterwasservideo || MP_134 || Echolotung || MP_135 || Seitensichtsonar, hochauflösendes Sedimentlot, Greiferproben mit anschließender Bestimmung der Korngrößenverteilung und Unterwasservideo |
|| MP_118 || durch Taucher oder per UV-Video |
|| MP_056 || Tiefengrenzen, Dichte, Biomasse, Artenzahl |
|| MP_037 || http://fino.bsh.de/blmpweb/kennblatt?id=6&kapitel=3&html=on#Zooplankton_32 (derzeit in Überarbeitung) || MP_041 || BLMP (2009) Prüfverfahren-SOP: Phytoplankton-Untersuchungen in Oberflächengewässern der Küste (qualitativ und quantitativ). Muster-Standardarbeitsanweisung für Laboratorien des Bund/Länder Messprogramms. Version 1, 69 S. |
|| MP_039 || |
|| MP_108, MP_109 || |
|| MP_044 || |
|| MP_037 || http://fino.bsh.de/blmpweb/kennblatt?id=6&kapitel=3&html=on#Zooplankton_32 (derzeit in Überarbeitung) || MP_041 || BLMP (2009) Prüfverfahren-SOP: Phytoplankton-Untersuchungen in Oberflächengewässern der Küste (qualitativ und quantitativ). Muster-Standardarbeitsanweisung für Laboratorien des Bund/Länder Messprogramms. Version 1, 69 S. |
|| MP_039 || |
|| MP_021 || Probenahme-Methoden für Gesamt-N, Ammonium, Nitrat, Gesamt-P, Phosphat, Silikat || MP_033 || Method of sampling: Samples are collected using a CTD system which is attached to a rosette sampler. Oxygen sample must be the first taken from the water sampler and the reagents should be added immediately. Oxygen samples may be stored for up to 24 hours after adding the reagents and after complete fixation. The bottles should be kept in the dark and any change in temperature should be avoided. The basic method for the determination of oxygen concentration is the Winkler method (Grasshoff et al., 1983). In addition oxygen sensors at the CTD can be used. However, they have to be validated with discrete Winkler titration values. |
|| MP_035 || Messung der Sichttiefe mit Hilfe einer Secchi-Scheibe || MP_107 || Das Bundesamt für Seeschifffahrt und Hydrographie (BSH) betreibt in seinem Marinen Umweltmessnetz in Nord- und Ostsee (MARNET) derzeit elf automatische Messstationen. Erfassung durch autonome Messgeräte || MP_110 || In-situ Daten werden auf Schiffen und festen Plattformen in der Regel mit einer CTD erfasst.
Die genutzten Satelliten sind mit speziellen Sensoren ausgerüstet, aus deren Messwerten sich die Oberflächentemperatur ableiten läßt. Fernerkundungsdaten || MP_127 || In-situ Daten werden auf Schiffen und festen Plattformen in der Regel mit einer CTD erfasst.
Die genutzten Satelliten sind mit speziellen Sensoren ausgerüstet, aus deren Messwerten sich die Oberflächentemperatur ableiten läßt. |
Not relevant |
This program is registering all birds by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch of breeding or wintering birds by is mainly registration if the bird is catch in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of birds. |
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals. |
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals. |
The method can be seen in the manual. No age are estimated but length and weight. The data can be used to evaluate the development in the length and weight distribution for commercial species over time, as the gears are standardized. |
Other parameter measured in connection to health is condition in the demersal species. This is monitored over time to detect changes in health. Furthermore a subset of herring is analysed for dioxin and are also are also analysed for the parasite nematode Anasaki in the laboratory. |
Finland carries out all monitoring of seals by surveys from air crafts. Finland records occasional observations of Harbour Porposes to a HELCOM database (http://www.helcom.fi/baltic-sea-trends/data-maps/habitat/harbour-porpoise/) |
Monitoring of shallow seabed habitats has been started in the Finnish underwater mapping program VELMU. The VELMU-program provides baseline habitat maps for the basis of future monitoring. The monitoring methods are described in the HELCOM Monitoring manual (see above). |
Time series started before 2002 are carried out according to the Swedish monitoring method described in "Provfiske med kustöversikttsnät, nätlänkar och ryssjor ". |
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| Q9e - Quality assurance |
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| Q9f - Quality control | RealandDelayedValidation |
OtherQC |
Unknown |
Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
Unknown |
Unknown |
RealValidation |
RealValidation |
OtherQC |
Unknown |
RealValidation |
RealValidation |
OtherQC |
RealValidation |
OtherQC |
OtherQC |
Unknown |
Unknown |
Unknown |
OtherQC |
OtherQC |
OtherQC |
OtherQC |
OtherQC |
OtherQC |
RealandDelayedValidation |
DelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
DelayedValidation |
RealandDelayedValidation |
Unknown |
OtherQC |
OtherQC |
Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
DelayedValidation |
Unknown |
DelayedValidation |
DelayedValidation |
OtherQC |
DelayedValidation |
DelayedValidation |
DelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
Unknown |
RealandDelayedValidation |
Unknown |
Unknown |
RealValidation |
RealandDelayedValidation |
Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
Unknown |
Unknown |
Unknown |
DelayedValidation |
RealValidation |
DelayedValidation |
Unknown |
Unknown |
Unknown |
OtherQC |
RealandDelayedValidation |
OtherQC |
OtherQC |
OtherQC |
Unknown |
OtherQC |
Unknown |
DelayedValidation |
DelayedValidation |
OtherQC |
Unknown |
Unknown |
RealValidation |
DelayedValidation |
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| Q9g - Spatial resolution of sampling | Q9g - Proportion of area covered % | 100 |
0 |
100 |
0 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
0 |
100 |
100 |
100 |
100 |
70 |
100 |
100 |
100 |
100 |
50 |
100 |
50 |
100 |
10 |
2 |
2 |
2 |
0.3 |
2 |
100 |
100 |
2 |
50 |
100 |
90 |
90 |
90 |
100 |
10 |
50 |
100 |
100 |
15 |
100 |
100 |
100 |
63 |
50 |
100 |
50 |
20 |
100 |
39 |
10 |
100 |
100 |
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| Q9g - No. of samples | || MP_130 || 3 Meeresenten-Befliegungen, 5 Seevogel-Transektflüge (jährliche Teil-Surveys), 9 Wasservogelzählungen (Sep. – Apr.), 3 Brutbestandserfassungen pro Art |
|| MP_132 || offen, Schweinswal: alle 2 Jahre Bestandserfassung und Jungtieranteil westliche Ostsee, ganzjährig POD-Monitoring östliche Ostsee, Robben: mind. 12 Liegeplatzerfassung |
|| MP_131 || Offen. Untersuchung aller Wal- und Kegelrobbentotfunde |
|| MP_132 || offen, Schweinswal: alle 2 Jahre Bestandserfassung und Jungtieranteil westliche Ostsee, ganzjährig POD-Monitoring östliche Ostsee, Robben: mind. 12 Liegeplatzerfassung |
|| MP_056, MP_118, MP_119, MP_129 || 5-20 |
|| MP_119 || 5-20 |
|| MP_031 || Für diese Messungen lassen sich keine genauen Regelprobenzahlen angeben. || MP_135 || die Probenzahl hängt stark von den Ergebnissen der hydroakustischen Karierung ab |
|| MP_031 || Für diese Messungen lassen sich keine genauen Regelprobenzahlen angeben. || MP_134 || Bei der hydrographischen Vermessung werden keine Proben entnommen || MP_135 || die Probenzahl hängt stark von den Ergebnissen der hydroakustischen Karierung ab |
|| MP_118 || 5-20 |
|| MP_056 || 5-20 |
|| MP_037 || || MP_041 || >100
Beim Monitoring der offenen See (BSH-finanziert, hauptsächlich Bereich der AWZ) Zielwert von 55 Probenahmen, meist aus je 2 Tiefen, also insgesamt maximal 110 Proben pro Jahr. Monitoring der Küstengewässer MV: ca. 100 Proben pro Jahr. Monitoring der Küstengewässer SH ca 180 Proben pro Jahr. |
|| MP_039 || >100
Beim Monitoring der offenen See (BSH-finanziert, hauptsächlich Bereich der AWZ) Zielwert von 55 Probenahmen, meist aus je 2 Tiefen, also insgesamt maximal 110 Proben pro Jahr. Monitoring der Küstengewässer MV: ca. 100 Proben pro Jahr. Monitoring der Küstengewässer SH ca 180 Proben pro Jahr. |
|| MP_108 || Jährliche Berechnung der Emissionen; diese fließen in die EMEP-Berichte ein; HELCOM fordert jährlich einen EMEP-Bericht an || MP_109 || EMEP modelliert 1x jährlich, gemessen wird an den 2 Messstationen wöchentlich, die Messdaten werden zur Validierung des Modells genutzt; HELCOM fordert jährlich einen EMEP-Bericht an; OSPAR hat den letzten Bericht 2007 angefordert (Daten 1990-2004), gegenwärtig gibt es keine Einigkeit unter der OSPAR-Vertragsstaaten ob für die nächste Anwendung der COMP in 2016 ein neuer Bericht angefordert werden soll; Deutschland setzt sich bei OSPAR dafür ein, scheitert aber am Widerstand der anderen Vertragsstaaten; momentan fehlen deshalb detaillierte Auswertungen für die Nordsee |
|| MP_044 || 12-13 |
|| MP_037 || || MP_041 || >100
Beim Monitoring der offenen See (BSH-finanziert, hauptsächlich Bereich der AWZ) Zielwert von 55 Probenahmen, meist aus je 2 Tiefen, also insgesamt maximal 110 Proben pro Jahr. Monitoring der Küstengewässer MV: ca. 100 Proben pro Jahr. Monitoring der Küstengewässer SH ca 180 Proben pro Jahr. |
|| MP_039 || >100
Beim Monitoring der offenen See (BSH-finanziert, hauptsächlich Bereich der AWZ) Zielwert von 55 Probenahmen, meist aus je 2 Tiefen, also insgesamt maximal 110 Proben pro Jahr. Monitoring der Küstengewässer MV: ca. 100 Proben pro Jahr. Monitoring der Küstengewässer SH ca 180 Proben pro Jahr. |
|| MP_021 || BSH: ca. 240-320 Proben; LLUR: ca. 54 Proben; NLWKN: ca. 68 Proben
Siehe auch: http://fino.bsh.de/blmpweb/kennblatt?id=25&kapitel=3&html=on (derzeit in Überarbeitung)
(Stand 2011; derzeit in Überarbeitung) || MP_033 || >100
The depths at which sampling should take place are as follows (in metres): 1, 5, 10, 15, 20, (25)*, 30, 40 and as close to the bottom as possible (preferably less than 1 metre from the sediment surface to get near bottom oxygen concentration). For unstratified water less than 10m depth, samples will be taken from 1m. The regional conditions and circumstances have to be considered, when choosing the sampling depth. |
|| MP_035 || >100 || MP_107 || Es handelt sich um Dauermessungen || MP_110 || Es werden keine Proben entnommen || MP_127 || Die Probenzahl hängt von der Anzahl der möglichen Messfahrten ab. |
One |
Individual records of bird species and bird flocks are recorded. |
Not determined - passive sampling. |
Not determined - passive sampling. |
as described above |
For the Belt Sea area it is 1/5-6 years. |
For the Belt Sea population it is 1/5-6 years. For the Baltic Sea population there is no regular schedule as the monitoring method has just been established. |
For the Natura2000 areas it is 1/3years. |
Sidescan data is gatherered covering most of the bottom of the mapped Natura 2000 sites. Number of videosamles vary |
18% of the total vessels operating in this area were above 12 meters in 2013. |
around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected species for age. |
Around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected species for age. |
Around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected speces for age. |
around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%.
From minimum 1 station per day we sample all species with length and weight and only selected speces for age. |
840 - 1680
12-24 annual samples at each location
approx. 70 stations |
Both model calculations and measurements covers the entire callendar year. |
Not determined - passive sampling. |
around 50 trips are conducted on an annual basis and this corrispond to 55 days at sea.- Indicating that 1 trip equals to 2%
From minimum 1 station per day we sample all species with length and weight and only selected species for age. |
3 |
as described above |
5 |
Measurements covers the entire callendar year. The estimated despositions for deposition to Danish land areas and Inner Dansih Waters are total annual deposition. |
2 samples/station/year
direct outlet: 12 stations
indirect outlet: 9 stations |
4 |
10 |
HELCOM Monitoring manual - Sub-programme: Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ |
HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution |
Observations made by the public and by the birding people are collected from the whole Finnish coastal and open sea area (Aland islands
included). The bird monitoring observation network includes several important Razorbill- and tern colonies. |
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
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: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance |
HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status |
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna .
HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics |
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna .
HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics |
HELCOM Monitoring manual - Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species .
HELCOM Monitoring manual - Sub-programme: Habitat forming species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/habitat-forming-species-and-substrates .
HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/stc/files/CombineManual/PartC/AnnexC9.pdf |
Monitoring of all activities is done in all Finnish coastal areas (all sub-basins). |
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 |
240 km/metus (60 km apskaitų 4 kartus per sezoną) |
apie 2500 km transektų (860 km ilgio transektų su trim pakartojimais) |
85 nests visited 3 times a year. |
Phytoplankton - 90/year
Zooplankton - 93/year |
120 counting units annually. |
Approximately 410 counting units annually. In addition, country wide survey are carried out at irregular intervals, the last in 2004 |
Details about breeding sites are not available, but all known sites are included in monitoring |
Approximate number of samples expected to be taken from the assessment area and Proportion of geographic scope covered by sampling is also unknown since it depends on the activity of the commercial fishery. |
Approximate number of samples expected to be taken from the assessment area and Proportion of geographic scope covered by sampling is unknown since it is difficult to estimate. |
1 sample from 12 locations = 12 samples/year |
25 samples from 3 locations = 75 samples/year |
Seals found dead each day, all year, and hunted grey seals collected during hunting season (15 April- 31 December); hence number varies. Geographic scope depends on found and reported dead seals, as well as hunted seals; hence it varies. |
1 count per year a week during the moult |
100 acoustic locations during 2, 5 years (2011-2013). No information regarding the next survey. |
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| Q9i - Description of sample representivity | Es erfolgt eine flächendeckende hydroakustische Kartierung der Meeresbodensubstrate |
Es erfolgt eine flächendeckende hydroakustische Kartierung der Meeresbodensubstrate |
For the species Sandwich Tern and Little Tern under the programme NOVANA: Every 3rd year.
For the species Arctic Tern and Common Tern under the programme NOVANA: Every 6th year
For Great Cormorant: Every year.
For gulls and terns in the Danish part of the Wadden Sea: Every year. |
103 fishermen are participating with 3 sites eac. Indicating that each site represent 0.3% of the total.
In total 52,000 individuals were caught in the last three year. Eelpout topped the list of species most frequently caught, mostly in fyke-nets. Next on the list was flounder with 23,000 individuals being caught over 3 years. An equal number of cod and eel were caught; 9,000 individuals. |
According to EU Directive 2006/7 / EC of 15 February 2006 on bathing water quality, sample taking will only take place in the "bathing season" (Denmark 1. of June to 1. of September / in some cases to 15. of September) and only were there are a "large number" of bathers. Link to Directive:
http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:064:0037:0051:EN:PDF.
Please find also link to the Danish Statutory order concerning bathing water:
https://www.retsinformation.dk/forms/R0710.aspx?id=143189. Please find link to the Reporting Sheet from EEA (European Environment Agency) : http://rod.eionet.europa.eu/obligations/531. |
Approx. 50% of the catchment area is covered by monitoring stations. The locations are selected mainly to cover the largest rivers and to be distributed across the entire country. The nutrient load from the remaining catchment area is estimated using models.
840 - 1680
12-24 annual samples at each location in approx. 70 stations |
variation in relation to risk across the area |
The stations are for most parts used to give a spatial more than time-trend view of concentrations/pressures within different marine areas. Some stations are analysed in duplicates from two subsamples at the same location, others are sampled within the same area in relative close proximity to give an estimate of the area variance. |
Information on the following activities is collected at HELCOM level: RenewableEnergy, MiningSandGravel, Dredging, Ports, CablesPipelines, OffshoreStructures, Shipping and SolidWasteDisposal.
See under "Action areas" at: http://www.helcom.fi/action-areas |
Information on the activity Fisheries is collected at HELCOM level. See under "Action areas" at: http://www.helcom.fi/action-areas |
Monitoring will be carried out in three areas three times a year. |
no variations |
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 |
In Puck Bay the monitoring is performed 12 times a year. |
The realization of sub-programme is dependant on the financing from the LIFE + project. |
See sub-programme Häckande sjöfågel, chapter Rumslig och tidsmässig täckning |
See sub-programme Övervintrande sjöfågel, chapter Rumslig och tidsmässig täckning" |
See sub-programme Reproduktion hos havsörn, chapter Rumslig och tidssmässig täckning.
See sub-programme Reproduktion hos havsörn, parameter table. |
See sub-programme Migrerande fisk - ål, parameter table and chapter Rumslig och tidsmässig täckning |
See sub-programme Migrerande fisk - Lax, parameter table and chapter Rumslig och tidsmässig täckning |
See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning |
See sub-programme Hälsotillstånd hos kustfisk, chapter Rumslig och tidsmässig täckning |
Found drowned animals are collected every day the whole year and samples from animals are also collected during hunting season: April 15- December 31 |
See sub-programme Bestånd av säl, the parameter table and chapter Rumslig och tidsmässig täckning and Metoder (QA/QC) |
See sub-programme Bestånd av tumlare, chapter Rumslig och tidsmässig täckning
See sub-programme Bestånd av tumlare, parameter table. |
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| Q10a - Scale for aggregation of data |
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| Q10b - Other scale for aggregation of data | || MP_130 || Deutsche Hoheitsgewässer (AWZ + Küstengewässer) |
|| MP_132 || Deutsche Hoheitsgewässer (AWZ + Küstengewässer), MINOS-Zählgebiete || Additional Data || Other |
|| MP_131 || Deutsche Ostseeküsten (AWZ + Küstengewässer) || Additional Data || Other |
|| MP_132 || Deutsche Hoheitsgewässer (AWZ + Küstengewässer), MINOS-Zählgebiete || Additional Data || Other |
|| MP_056, MP_118, MP_119, MP_129 || || Additional Data || Unknown, Other |
|| MP_119 || Wasserkörper || Additional Data || Other |
|| MP_031, MP_135 || |
|| MP_031, MP_134, MP_135 || |
|| MP_118 || Wasserkörper || Additional Data || Other |
|| MP_056 || |
|| MP_037 || Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. || MP_041 || || Additional Data || Other |
|| MP_039 || Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. || Additional Data || Other |
|| MP_108 || Emissionen werden pro Land erfasst || MP_109 || || Additional Data || Other, EU, Region, Subregion |
|| MP_044 || |
|| MP_037 || Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. || MP_041 || || Additional Data || Other |
|| MP_039 || Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. || Additional Data || Other |
|| MP_021 || Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. || MP_033 || || Additional Data || Other |
|| MP_035, MP_107, MP_110, MP_127 || || Additional Data || Other, Unknown, Region, Subregion |
For terns under the NOVANA programme corrections need to be made for incomplete coverage, however, in relation to the targets of the MSFD there is no further needs. |
Can be aggregated down to very local areas, as all records are georeferenced and entered into Geodatabase. |
The abundance of harbour seals should be aggregated in the four Danish management units. For this region the Kattegat (partly covering region ANSDK and shared with Sweden) and the Western Baltic also shared with Sweden. For the grey seals the Dniah counts should be part of the count for all of the Baltic Sea. |
Porpoise abundance should be aggregated on population level to avoid movement between areas. For this region there is a Baltic and a Belt Sea population (expanding over both the ANSDK and BALDK). |
The population monitoring of harbour seals should be aggregated in the four Danish management units. For this region the Kattegat (partly covering region ANSDK and shared with Sweden) and the Western Baltic also shared with Sweden. For the grey seals the Dniah counts should be part of the count for all of the Baltic Sea. |
Porpoise abundance should be aggregated on population level to avoid movement between areas. For this region there is a Baltic and a Belt Sea population (expanding over both the ANSDK and BALDK) |
Each land site is monitored, but none of the marine habitats. |
Data are collected for each Natura 2000 site. |
Currently the definitions of the habitat types are not agreed on between countries,. The definition fits within the definition described in the habitatsdirective, but could still vary from country to country. However, if other countries have similar maps produced an overall view of the the distribution of habitat types should be possible. Danish data is currently used for fisheries regulation in an international setting - where other countries have fishing rights in Danish waters. |
Because the Baltic sea bird individuals belong to the same population, co-operation between the HELCOM states would be important. However, only a little co-operation has occurred in the Baltic Sea region so far . |
Neighboring countries do not have this sub-programme |
The only significant river spawning White Fish populations occur in the Bothnian Bay |
See sub-programme Häckande sjöfågel, chapter Metoder |
Since the surveys are part of an international project, Swedish data can be aggregated with the other participating countries' data at different geographical levels. |
See sub-programme Reproduktion hos havsörn, chapter Metoder |
See sub-programme Hälsotillstånd hos kustfisk, chapter Metoder |
See sub-programme Hälsotillstånd hos säl, chapter Metoder |
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| Q10c - Access to monitoring data | Q10c - Data type | DataProducts |
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| Q10c - Data access mechanism | LocationInternationalDC |
LocationInternationalDC |
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URLview |
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| Q10c - Data access rights | Open |
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RestrictedSpecific |
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Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Q10c - INSPIRE standard | || MP_130 || || Additional Data || EnvMonitoringFacilities |
|| MP_132 || || Additional Data || EnvMonitoringFacilities |
|| MP_131 || || Additional Data || EnvMonitoringFacilities |
|| MP_132 || || Additional Data || EnvMonitoringFacilities |
|| MP_056, MP_118, MP_119, MP_129 || || Additional Data || EnvMonitoringFacilities |
|| MP_119 || || Additional Data || EnvMonitoringFacilities |
|| MP_031, MP_135 || || Additional Data || EnvMonitoringFacilities |
|| MP_031, MP_134, MP_135 || || Additional Data || EnvMonitoringFacilities |
|| MP_118 || || Additional Data || EnvMonitoringFacilities |
|| MP_056 || || Additional Data || EnvMonitoringFacilities |
|| MP_037, MP_041 || || Additional Data || EnvMonitoringFacilities |
|| MP_039 || || Additional Data || EnvMonitoringFacilities |
|| MP_108, MP_109 || || Additional Data || EnvMonitoringFacilities |
|| MP_044 || || Additional Data || EnvMonitoringFacilities |
|| MP_037, MP_041 || || Additional Data || EnvMonitoringFacilities |
|| MP_039 || || Additional Data || EnvMonitoringFacilities |
|| MP_021, MP_033 || || Additional Data || EnvMonitoringFacilities |
|| MP_035, MP_107, MP_127 || || Additional Data || EnvMonitoringFacilities || MP_110 || || Additional Data || OceanographicFeatures || unknown || SeaRegions |
HabitatsBiotopes SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
OceanographicFeatures SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
HabitatsBiotopes OceanographicFeatures SpeciesDistribution |
HabitatsBiotopes SeaRegions SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes OceanographicFeatures |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions |
HabitatsBiotopes SpeciesDistribution |
OceanographicFeatures SeaRegions |
OceanographicFeatures |
OceanographicFeatures SeaRegions |
HabitatsBiotopes OceanographicFeatures |
SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
SpeciesDistribution |
SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
Geology HabitatsBiotopes SpeciesDistribution |
SpeciesDistribution |
SpeciesDistribution |
EnvMonitoringFacilities |
SpeciesDistribution |
ManagementZonesReportingUnits |
EnvMonitoringFacilities |
EnvMonitoringFacilities |
EnvMonitoringFacilities |
EnvMonitoringFacilities |
EnvMonitoringFacilities |
EnvMonitoringFacilities |
EnvMonitoringFacilities |
EnvMonitoringFacilities |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Q10c Date data are available | 2015-01 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2013-09 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2015-01 |
2014-12 |
2013-10 |
2014-12 |
2014-12 |
2015-12 |
2014-11 |
2014-11 |
2014-11 |
2014-11 |
2014-11 |
2014-11 |
2014-12 |
2015-04 |
2015-04 |
2015-04 |
2014-10 |
2015-04 |
2015-04 |
2015-04 |
2015-10 |
2015-04 |
2014-12 |
2014-12 |
2014-12 |
2015-04 |
2014-12 |
1990-01 |
2014-12 |
2015-04 |
2015-04 |
2014-12 |
2015-12 |
2015-04 |
2015-04 |
1990-01 |
2014-12 |
2014-12 |
1999-01 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2015-12 |
2016-06 |
2016-06 |
2014-12 |
2015-12 |
2015-12 |
2015-12 |
2017-01 |
2015-12 |
2019-12 |
2015-12 |
2015-12 |
2016-01 |
2014-01 |
2014-09 |
2014-09 |
2014-09 |
2014-09 |
2014-09 |
2014-09 |
2014-09 |
2014-09 |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Q10c - Data update frequency | Other |
Other |
Other |
Other |
Yearly |
Yearly |
6yearly |
6yearly |
Yearly |
Yearly |
Unknown |
Other |
Yearly |
Yearly |
Unknown |
Other |
Yearly |
Yearly |
Yearly |
3yearly |
Asneeded |
Yearly |
Asneeded |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
2yearly |
3monthly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
2weekly |
2weekly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Asneeded |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Asneeded |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
6yearly |
Yearly |
Yearly |
Yearly |
2yearly |
Yearly |
Yearly |
Yearly |
Yearly |
6yearly |
Yearly |
3yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Other |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Q10d - Description of data access |
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Wie im Rahmen der Umsetzung von Artikel 19.3 der MSRL im CIS-Prozess abgestimmt, werden alle Daten und Produkte via Metadaten im nationalen Metadatenkatalog (http://geoportal.bafg.de/wasserblick-csw-client/?lang=de&page=1&searchtext=&hits=50&service=1&modell=1&data=1&...
|
Data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
In addition, aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
All current mapping projects has been combined: http://miljoegis.mim.dk/cbkort?&profile=natura2000planer2basis2013 Additionally the individual mapping projects are available in separat paper reports such as:
http://www2.nst.dk/Download/Udgivelser/N2000_Marin_raastof_naturtypekort_kattegat_oestersoe_2011.pdfand as interactive URL sites: http://www2.naturstyrelsen.dk/habitatkortlaegning/ |
http://www.miljoeportal.dk/Sider/Forside.aspx, in addition aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
http://www.miljoeportal.dk/Sider/Forside.aspx, in addition aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
http://www.miljoeportal.dk/Sider/Forside.aspx.
In addition, aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is available and can be requested. As both logbook data and VMS data is realtime and online the data can be made available on request.
Do to the law on personal data, the data is only made available in aggregated form. In addition, aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB), as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB) as well as in the forthcoming MSFD art 8 initial assessment due in 2018.. |
In ICES Regional data base (RDB) as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
A national data base is holding the data, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB).as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data is sent to the EC / EEA by the end of December each year
In addition aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
http://www.miljoeportal.dk/Sider/Forside.aspx, in addition aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
http://www.miljoeportal.dk/Sider/Forside.aspx, in addition aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
http://www.miljoeportal.dk/Sider/Forside.aspx, in addition aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Aggregated data is contained in yearly progress report published under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
In addition, aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES DATRAS database. In addition, aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
In ICES Regional data base (RDB). In addition, aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
Aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Aggregated data is reported in the forthcoming MSFD art 8 initial assessment due in 2018. |
Aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data will be reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA and in the forthcoming MSFD article 8 initial assessment in 2018 |
Aggregated data is reported in yearly reports under the National Monitoring Programme for Water and Nature, NOVANA, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
HELCOM CORE indicator - Abundance of waterbirds in the wintering season: http://www.helcom.fi/baltic-sea-trends/biodiversity/indicators/abundance-of-waterbirds-in-the-wintering-season/
Data is also available upon request from the Finnish Museum of Natural History (LUOMUS) - http://www.luomus.fi/en/species-distribution-and-biogeography
A summary showing the occurrence of breeding birds by species (based on the "Third Finnish Breeding Bird Atlas") is available at: http://atlas3.lintuatlas.fi/results/specieslist |
HELCOM CORE indicator - Abundance of waterbirds in the wintering season: http://www.helcom.fi/baltic-sea-trends/biodiversity/indicators/abundance-of-waterbirds-in-the-wintering-season/
Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution |
By request
|
HELCOM CORE indicator - MARINE BIRD HEALTH: http://www.helcom.fi/baltic-sea-trends/biodiversity/indicators/white-tailed-eagle-productivity/
Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
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 - http://helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Population_growth_rate_abundance_and_distribution_of_marine_mammals.pdf
Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance |
HELCOM CORE indicator - Pregnancy rates of the marine mammals-Particular emphasis on Baltic grey and ringed seals: http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Pregnancy_rates_of_marine_mammals.pdf
HELCOM CORE indicator - Nutritional status of seals: http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Nutritional_status_of_seals.pdf
Essential information about data access is available in the HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status |
HELCOM CORE indicator - State of the soft-bottom macrofauna communities - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator_State_of_the_soft-bottom_macrofauna_communities.pdf
OIVA public web portal on environmental information (in Finnish) - www.ymparisto.fi/oiva
OIVA is linked to the Finnish benthos database POHJE
Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
HELCOM CORE indicator - State of the soft-bottom macrofauna communities - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator_State_of_the_soft-bottom_macrofauna_communities.pdf
OIVA public web portal on environmental information (in Finnish) - www.ymparisto.fi/oiva
OIVA is linked to the Finnish benthos database POHJE
Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
HELCOM CORE indicator - Population structure of long-lived macrozoobenthic species http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator_Population_structure_of_long-lived_macrozoobenthic_species.pdf
OIVA public web portal on environmental information (in Finnish) - http://www.ymparisto.fi/oiva
OIVA is linked to the Finnish benthos database POHJE
Essential information on data access is available in the HELCOM Monitoring manual:
Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species (NOT COORDINATED)
Sub-programme: Soft bottom flora - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-flora |
OIVA public web portal on environmental information (in Finnish) - http://www.ymparisto.fi/oiva |
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 |
under development
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Under development
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Gathered monitoring data is stored in databases at Environmental Protection Agency and Nature Research Centre (http://www.gamtostyrimai.lt/en/). |
Through the following link:
http://www.monitoringptakow.gios.gov.pl/baza-danych |
The data will be available through
http://www.monitoringptakow.gios.gov.pl/baza-danych |
via EEA EIONET
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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. |
Direct encoding and sending to EEA and ICES database. |
Via HELCOM - ICES data portal
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EEA EIONET for the WFD monitoring.
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Via HELCOM - ICES database.
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See sub-programme Övervintrande sjöfågel, chapter Var finns data, and Metoder
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See sub-programme Övervintrande sjöfågel, chapter Var finns data
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See sub-programme Reproduktion hos havsörn, chapter Var finns data
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See sub-programme Migrerande fiskarter - ål, chapter Var finns data
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See sub-programme Migrerande fiskarter - lax, chapter Var finns data
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See sub-programme Kustprovfiske, chapter Var finns data
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See sub-programme Hälsotillstånd hos kustfisk, chapter Var finns data
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Se sub-programme Hälsotillstånd hos säl, chapter Var finns data
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See sub-programme Bestånd av säl, chapter Var finns data
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See sub-programme Bestånd av tumlare, chapter Var finns data
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