Art11

Member State report / Art11 / 2014 / D4 / 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	D4 Food webs/D1 Ecosystems
Region/subregion	Baltic
Reported by	Reporter not found

Simplified table

Member state		DE	DE	DE	DE	DE	DE	DE	DE	DE	DE	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	FI	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LT	LV	LV	LV	LV	LV	LV	LV	PL	PL	PL	PL	PL	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE	SE
Monitoring programme	Monitoring programme name	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D3	MP_D3	MP_D3	MP_D3	MP_D3	MP_D5	MP_D5	MP_D5	MP_D5	MP_D5	MP_D5	MP_D7	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_SeabedHabitats	MP_D1_4_6_SeabedHabitats	MP_D1_4_6_SeabedHabitats	MP_D1_4_6_SeabedHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D2	MP_D2	MP_D2	MP_D2	MP_D2	MP_D2	MP_D2	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Fish	MP_D1_4_6_WaterColumnHabitats	MP_D3	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Birds	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Fish	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_Mammals	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D1_4_6_WaterColumnHabitats	MP_D3	MP_D3	MP_D3	MP_D3	MP_D3	MP_D3	MP_D3	MP_D3	MP_D3	MP_D3
Monitoring programme	Reference existing programme																																											BALFI-D01,04,06fis	BALFI-D01,04,06fis	BALFI-D01,04,06fis			BALFI-D01,04,06ben	BALFI-D01,04,06ben	BALFI-D01,04,06ben	BALFI-D01,04,06ben	BALFI-D01,04,06pel	BALFI-D01,04,06pel	BALFI-D01,04,06pel	BALFI-D01,04,06pel	BALFI-D01,04,06pel																																Baltic International Trawl Surveys (BITS)
Monitoring programme	Marine Unit ID											BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea																																BAL-PL-AA-27 BAL-PL-AA-38
Q4e - Programme ID		BALDE_Mon_016	BALDE_Mon_016	BALDE_Mon_016	BALDE_Mon_016	BALDE_Mon_016	BALDE_Mon_016	BALDE_Mon_017	BALDE_Mon_017	BALDE_Mon_017	BALDE_Mon_017	BALDK-FISH-D01-D04	BALDK-FISH-D01-D04	BALDK-FISH-D01-D04	BALDK-FISH-D01-D04	BALDK-FISH-D01-D04	BALDK-FISH-D01-D04	BALDK-FISH-D01-D04	BALDK-mammal-D01-04	BALDK-mammal-D01-04	BALDK-mammal-D01-04	BALDK-mammal-D01-04	BALDK-mammal-D01-04	BALDK-mammal-D01-04	BALDK-D01	BALDK-D01	BALDK-D03	BALDK-D03	BALDK-D03	BALDK-D03	BALDK-D03	BALDK-D05	BALDK-D05	BALDK-D05	BALDK-D05	BALDK-D05	BALDK-D05	BALDK-D07	BALFI-D01,04,06bir	BALFI-D01,04,06bir	BALFI-D01,04,06bir	BALFI-D01,04,06bir	BALFI-D01,04,06bir	BALFI-D01,04,06fis	BALFI-D01,04,06fis	BALFI-D01,04,06fis	BALFI-D01,04,06mam	BALFI-D01,04,06mam	BALFI-D01,04,06ben	BALFI-D01,04,06ben	BALFI-D01,04,06ben	BALFI-D01,04,06ben	BALFI-D01,04,06pel	BALFI-D01,04,06pel	BALFI-D01,04,06pel	BALFI-D01,04,06pel	BALFI-D01,04,06pel	BALLT-D01234-2	BALLT-D01234-2	BALLT-D01234-2	BALLT-D01234-2	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BALLT-D02457-1	BAL-LV-2014	BAL-LV-2014	BAL-LV-2014	BAL-LV-2014	BAL-LV-2014	BAL-LV-2014	BAL-LV-2014	BALPL-D0104_Birds	BALPL-D0104_Birds	BALPL-D0104_Fish	BALPL-D0104_WaterColumnHabitats	BALPL-D03	BALSE-Birds-D14	BALSE-Birds-D14	BALSE-Birds-D14	BALSE-Birds-D14	BALSE-Birds-D14	BALSE-Birds-D14	BALSE-Fish-D14	BALSE-Fish-D14	BALSE-Fish-D14	BALSE-Fish-D14	BALSE-Fish-D14	BALSE-Fish-D14	BALSE-Fish-D14	BALSE-Fish-D14	ANSSE-mammals-D14	ANSSE-mammals-D14	ANSSE-mammals-D14	ANSSE-mammals-D14	ANSSE-mammals-D14	ANSSE-mammals-D14	BALSE-PEL-D14	BALSE-PEL-D14	BALSE-PEL-D14	BALSE-PEL-D14	BALSE-PEL-D14	BALSE-PEL-D14	BALSE-PEL-D14	BALSE-PEL-D14	BALSE-PEL-D14	BALSE-PEL-D14	BALSE-COMFISH-D3	BALSE-COMFISH-D3	BALSE-COMFISH-D3	BALSE-COMFISH-D3	BALSE-COMFISH-D3	BALSE-COMFISH-D3	BALSE-COMFISH-D3	BALSE-COMFISH-D3	BALSE-COMFISH-D3	BALSE-COMFISH-D3
Q4f - Programme description		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 den Monitoringprogrammen zu den Deskriptoren D2, D3, D5, D6, D7, D8, D10 und D11 erfasst. Die Abundanz ist ein grundlegend ökologischer Parameter, welcher auch die Auswirkungen neu entstehender Belastungen aufgreifen sollte.	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 den Monitoringprogrammen zu den Deskriptoren D2, D3, D5, D6, D7, D8, D10 und D11 erfasst. Die Abundanz ist ein grundlegend ökologischer Parameter, welcher auch die Auswirkungen neu entstehender Belastungen aufgreifen sollte.	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 den Monitoringprogrammen zu den Deskriptoren D2, D3, D5, D6, D7, D8, D10 und D11 erfasst. Die Abundanz ist ein grundlegend ökologischer Parameter, welcher auch die Auswirkungen neu entstehender Belastungen aufgreifen sollte.	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 den Monitoringprogrammen zu den Deskriptoren D2, D3, D5, D6, D7, D8, D10 und D11 erfasst. Die Abundanz ist ein grundlegend ökologischer Parameter, welcher auch die Auswirkungen neu entstehender Belastungen aufgreifen sollte.	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 den Monitoringprogrammen zu den Deskriptoren D2, D3, D5, D6, D7, D8, D10 und D11 erfasst. Die Abundanz ist ein grundlegend ökologischer Parameter, welcher auch die Auswirkungen neu entstehender Belastungen aufgreifen sollte.	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 den Monitoringprogrammen zu den Deskriptoren D2, D3, D5, D6, D7, D8, D10 und D11 erfasst. Die Abundanz ist ein grundlegend ökologischer Parameter, welcher auch die Auswirkungen neu entstehender Belastungen aufgreifen sollte.	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 HELCOM PLC Berichterstattung werden unterschiedliche Belastungssituationen identifiziert, so dass das Monitoring entsprechend differenziert erfolgen kann.	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 HELCOM PLC Berichterstattung werden unterschiedliche Belastungssituationen identifiziert, so dass das Monitoring entsprechend differenziert erfolgen kann.	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 HELCOM PLC Berichterstattung werden unterschiedliche Belastungssituationen identifiziert, so dass das Monitoring entsprechend differenziert erfolgen kann.	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 HELCOM PLC Berichterstattung werden unterschiedliche Belastungssituationen identifiziert, so dass das Monitoring entsprechend differenziert erfolgen kann.	The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function.Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.	The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function.Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.	The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function.Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.	The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function.Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.	The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function.Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.	The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function.Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.	The programme is focused on length of cod and saithe to follow the state of top predator fish and hence ecosystem function.Commercial fishing is monitored as the primary pressure. Other non-commercial fish are also monitored but no targets are set up. Cephalopods are also monitored but no targets are set up.	All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable. In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities.	All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable. In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities.	All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable. In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities.	All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable. In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities.	All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable. In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities.	All relevant marine mammals are monitored. The programme includes state/impact, pressures, activities and measures. The monitoring on harbour seals is focused on state and habitats as the population is well established and growing. The monitoring on grey seals is focused on state and habitats as the population is newly established and growing. The programme on Harbour porpoise is focused on state but also pressures and impacts as the population is relatively small and vulnerable. In case of relevant populations not beeing stabile og in progress further investigative monitoring will be initiated to identify causalities.	Monitoring of water cloumn habitats consists of the following sub-program Pelagic community characteristics (phytoplankton and zooplankton species composition, abundance and/or biomass. In addition water column relevant monitoring is performed in the program packages for eutrophication and biodiversity.	Monitoring of water cloumn habitats consists of the following sub-program Pelagic community characteristics (phytoplankton and zooplankton species composition, abundance and/or biomass. In addition water column relevant monitoring is performed in the program packages for eutrophication and biodiversity.	The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.	The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.	The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.	The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.	The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme is supplemented by programmes aiming at the documentation of incidental by-catches of birds and mammals in order to develop measures that may reduce incidental by-catches.	The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data.	The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data.	The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data.	The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data.	The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data.	The eutrophication programme is an integrated part of the National Monitoring Programme for Water and Nature, NOVANA that records physical, chemical and biological conditions. The overall structure of NOVANA is reflecting the principles of the DPSIR causal framework. The data provided by the eutrophication programme is traditionally considered in conjunction with data coming from several other programmes of the MSFD monitoring for instance plankton and benthos data.	The oceanographical monitoring programme of the Danish Meteorological Institute, DMI measures water level, tides, water temperature and currents that provide data for the forecast models of the DMI institute. The data supplements the general marine data collected in the framework of the existing environmental monitoring and is included in the marine models being developed under the National Monitoring Programme for Water and Nature, NOVANA. In the present BALDK-D07 programme on hydrological changes extraction operations are included as these may cause hydrographical changes. Major infrastructure works such as the fortcoming fixed link between Denmark and Germany is not included in the MSFD programme. A separate programme will be developed to control and monitor environmental status in relation to the environmental targets stipulated in the forthcoming Construction Bill for the fixed link across Fehmarn,	General information is available in the HELCOM Monitoring manual (Biodiversity-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-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-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-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-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 (Biodiversity, Fish) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Fish General information on Sub-programmes (Fish and Fisheries) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/	General information is available in the HELCOM Monitoring manual (Biodiversity, Fish) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Fish General information on Sub-programmes (Fish and Fisheries) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/	General information is available in the HELCOM Monitoring manual - 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 - 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 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 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 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 is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/	General information is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/	General information is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/	General information is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/	General information is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/	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. Indicators calculated using monitoring data are sufficiently sensitive and changes in population status are observed over the course of several years. The indicatorâs dependence on commercial fishing is sufficiently demonstrated in various marine regions and freshwaters. Fishing intensity as one of the main factors affecting coastal fish communities is monitored and regulated by legislation. The monitoring of fish communities reflects the effectiveness of these fisheries regulatory measures. In order to provide a reliable assessment of the status and composition of the Lithuanian coastal fish communities, monitoring is foreseen on an annual basis in different areas of the Baltic Sea.	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. Indicators calculated using monitoring data are sufficiently sensitive and changes in population status are observed over the course of several years. The indicatorâs dependence on commercial fishing is sufficiently demonstrated in various marine regions and freshwaters. Fishing intensity as one of the main factors affecting coastal fish communities is monitored and regulated by legislation. The monitoring of fish communities reflects the effectiveness of these fisheries regulatory measures. In order to provide a reliable assessment of the status and composition of the Lithuanian coastal fish communities, monitoring is foreseen on an annual basis in different areas of the Baltic Sea.	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. Indicators calculated using monitoring data are sufficiently sensitive and changes in population status are observed over the course of several years. The indicatorâs dependence on commercial fishing is sufficiently demonstrated in various marine regions and freshwaters. Fishing intensity as one of the main factors affecting coastal fish communities is monitored and regulated by legislation. The monitoring of fish communities reflects the effectiveness of these fisheries regulatory measures. In order to provide a reliable assessment of the status and composition of the Lithuanian coastal fish communities, monitoring is foreseen on an annual basis in different areas of the Baltic Sea.	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. Indicators calculated using monitoring data are sufficiently sensitive and changes in population status are observed over the course of several years. The indicatorâs dependence on commercial fishing is sufficiently demonstrated in various marine regions and freshwaters. Fishing intensity as one of the main factors affecting coastal fish communities is monitored and regulated by legislation. The monitoring of fish communities reflects the effectiveness of these fisheries regulatory measures. In order to provide a reliable assessment of the status and composition of the Lithuanian coastal fish communities, monitoring is foreseen on an annual basis in different areas of the Baltic Sea.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.	Fiziniai-cheminiai bei hidrologiniai-meteorologiniai parametrai svarbūs tiek pelagialės, tiek dugno buveinių ir bendrijų būklei interpretuoti (daugiau informacijos pdf ataskaitoje, 146 psl.). Hidrologiniai-meteorologiniai parametrai taip pat yra labai svarbūs klimato kaitai vertinti. Fitoplanktono rūšinė sudėtis, gausumas ir biomasė parodo bioįvairovės pokyčius ekosistemoje (mitybos tinkluose, pirminę produkciją ir pan.). Bakterioplanktonas yra svarbus maistinių medžiagų ciklo pokyčių rodiklis. Monitoringo rezultatai taip pat svarbūs eutrofikacijos vertinimui.								http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf	http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf	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	The Monitorng programme follows directly HELCOM COMBINE monitoring guidelines and is in line with MSFD reporting requirements.	The assessment of commercially exploited fish is performed in the frame of BITS surveys. At this stage the only assessed stocks are: cod, 2 flounder stocks, sprat and herring. There is still a need to set a monitoring programme in transitional waters and obtaining new data for the assessment of salmon, trout, and percisid species.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
Q5e - Natural variability		Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	ExpertOpinion Quantiative	ExpertOpinion Quantiative	ExpertOpinion Quantiative	ExpertOpinion Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	Qualitative Quantiative	Qualitative Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Qualitative Quantiative	Qualitative Quantiative	Qualitative Quantiative	Qualitative Quantiative	Qualitative Quantiative	Qualitative Quantiative	Qualitative Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Qualitative Quantiative	Qualitative Quantiative	Qualitative Quantiative	Quantiative	Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion Qualitative Quantiative	ExpertOpinion	ExpertOpinion	ExpertOpinion	ExpertOpinion	ExpertOpinion	ExpertOpinion	ExpertOpinion	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	ExpertOpinion	ExpertOpinion	ExpertOpinion	ExpertOpinion	ExpertOpinion	ExpertOpinion	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	ExpertOpinion Quantiative	ExpertOpinion Quantiative	ExpertOpinion Quantiative	ExpertOpinion Quantiative	ExpertOpinion Quantiative	ExpertOpinion Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative	Quantiative
Q5d - Adequacy for assessment of GES	Q5d - Adequate data	N	N	N	N	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	N	Y	Y	Y	Y	Y	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N
Q5d - Adequacy for assessment of GES	Q5d - Established methods	N	N	N	N	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	Y	Y	Y	N	Y	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y
Q5d - Adequacy for assessment of GES	Q5d - Adequate understanding of GES	Y	Y	Y	Y	Y	Y	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	Y	Y	Y	Y	Y	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y
Q5d - Adequacy for assessment of GES	Q5d - Adequate capacity	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y
Q5f - Description of programme for GES assessment		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 bestehenden Messprogramme als Zeitreihen zur Verfügung. Es gibt in der wissenschaftlichen Literatur vielfache Vorschläge zu der Bewertung von Indikatoren, die als Zeitserien vorliegen, hier muss jedoch auf nationaler und internationaler Ebene (HELCOM) eine Einigung über das Vorgehen zur Bewertung erzielt werden.	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 bestehenden Messprogramme als Zeitreihen zur Verfügung. Es gibt in der wissenschaftlichen Literatur vielfache Vorschläge zu der Bewertung von Indikatoren, die als Zeitserien vorliegen, hier muss jedoch auf nationaler und internationaler Ebene (HELCOM) eine Einigung über das Vorgehen zur Bewertung erzielt werden.	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 bestehenden Messprogramme als Zeitreihen zur Verfügung. Es gibt in der wissenschaftlichen Literatur vielfache Vorschläge zu der Bewertung von Indikatoren, die als Zeitserien vorliegen, hier muss jedoch auf nationaler und internationaler Ebene (HELCOM) eine Einigung über das Vorgehen zur Bewertung erzielt werden.	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 bestehenden Messprogramme als Zeitreihen zur Verfügung. Es gibt in der wissenschaftlichen Literatur vielfache Vorschläge zu der Bewertung von Indikatoren, die als Zeitserien vorliegen, hier muss jedoch auf nationaler und internationaler Ebene (HELCOM) eine Einigung über das Vorgehen zur Bewertung erzielt werden.	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 bestehenden Messprogramme als Zeitreihen zur Verfügung. Es gibt in der wissenschaftlichen Literatur vielfache Vorschläge zu der Bewertung von Indikatoren, die als Zeitserien vorliegen, hier muss jedoch auf nationaler und internationaler Ebene (HELCOM) eine Einigung über das Vorgehen zur Bewertung erzielt werden.	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 bestehenden Messprogramme als Zeitreihen zur Verfügung. Es gibt in der wissenschaftlichen Literatur vielfache Vorschläge zu der Bewertung von Indikatoren, die als Zeitserien vorliegen, hier muss jedoch auf nationaler und internationaler Ebene (HELCOM) eine Einigung über das Vorgehen zur Bewertung erzielt werden.	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.	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.	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.	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.	The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values	The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values	The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values	The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values	The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values	The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values	The programme provides data on key ndicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distances from levels recorded earlier and/or provide data for establishing of quantiative GES reference values	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf. Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” . DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf. Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” . DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf. Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” . DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf. Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” . DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf. Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” . DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf. Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Der er indgået aftale mellem Naturstyrelsen og Maersk Oil om et moniteringsprogram af havpattedyrs tilstedeværelse og adfærd i området, sammenholdt med støjpåvirkninger fra offshore-relaterede aktiviteter. Programmet startede i februar 2013 og forventes afsluttet i 2016. Forskningsprojektet (Ph.D. projekt), som udføres i samarbejde med Aarhus Universitet, ”Behavioural response of harbour porpoise to sound generated from routine operations in the oil and gas offshore industry” . DTU AQUA registrerer bifangst af marsvin. Der foretages kameraovervågning af bifangster i sydlig Kattegat og V. Østersø og andet bifangstdata. Det er et krav for de fiskere, der fisker under det bæredygtige fiskeri, at alle bifangster af fugle og havpattedyr rapporteres. Populationstællingen af marsvin foregår ved en kombination af et akustisk og visuelle survey (SCANS-metoden mm.). Populationstællinger i Nordsøen og Østersøen foretages i EU-projekter (SCANS og SAMBAH) uden for det nationale overvågningsprogram, da populationen af marsvin ’deles’ med Danmarks nabolande. Næste store tælling i hele Europa er planlagt til 2016 (SCANS III). SAMBAH projektet har til formål for første gang at få et estimat for antal og tætheder af marsvin i Østersøen. Bestandsestimat og kortlægning af habitat præferencer vha. akustiske data loggere (C-PODs).	The programme provides data on key indicators for descriptor 4. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.	The programme provides data on key indicators for descriptor 4. Existing data series will provide information on variability , trends and distance from levels recorded previously and/or provide data for establishing of quantitative GES reference values.	According to coordination in ICES	According to coordination in ICES	According to coordination in ICES	According to coordination in ICES	According to coordination in ICES	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for estblishing of quantitative GES reference values.	The general programme provides information to assess possible alternations og the physical environment. Th extration activity is regulated in detail in Statutory Order no. 1169 issued 3/10-2013. In addition to this separate programmes are prepared in relation to possible large scale construction activities at sea based on EIA-assessments.	The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.	The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.	The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.	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 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.	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.	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.	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.	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 supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.	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 1.7.1), the Community abundance index (predators) and the Community trophic index (indicators 4.2.1.). Methodological recommendations for the calculation of these indicators and data collection have been developed by HELCOM experts. For calculation purposes, the data shall be collected as part of the monitoring programme. The use of standardised studies over a number of years makes it possible to assess natural variations and to determine (expertly) the extent of anthropogenic exposure (variation of indicators and status depending on the intensity of known factors).	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 1.7.1), the Community abundance index (predators) and the Community trophic index (indicators 4.2.1.). Methodological recommendations for the calculation of these indicators and data collection have been developed by HELCOM experts. For calculation purposes, the data shall be collected as part of the monitoring programme. The use of standardised studies over a number of years makes it possible to assess natural variations and to determine (expertly) the extent of anthropogenic exposure (variation of indicators and status depending on the intensity of known factors).	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 1.7.1), the Community abundance index (predators) and the Community trophic index (indicators 4.2.1.). Methodological recommendations for the calculation of these indicators and data collection have been developed by HELCOM experts. For calculation purposes, the data shall be collected as part of the monitoring programme. The use of standardised studies over a number of years makes it possible to assess natural variations and to determine (expertly) the extent of anthropogenic exposure (variation of indicators and status depending on the intensity of known factors).	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 1.7.1), the Community abundance index (predators) and the Community trophic index (indicators 4.2.1.). Methodological recommendations for the calculation of these indicators and data collection have been developed by HELCOM experts. For calculation purposes, the data shall be collected as part of the monitoring programme. The use of standardised studies over a number of years makes it possible to assess natural variations and to determine (expertly) the extent of anthropogenic exposure (variation of indicators and status depending on the intensity of known factors).	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.	Kol kas nustatyti tik zooplanktono rodikliai: Irklakojų vėžiagyvių (Copepoda) grupės biomasė ir Zooplanktono mikrofagų biomasė. Šiame etape kitų rodiklių pagal kuriuos būtų galima vertinti buveinių būklę, o taip pat „gerą būklę“ nėra. Įgyvendinant ES Bendrąją vandens politikos direktyvą yra pateikti preliminarūs pasiūlymai dėl fitoplanktono, tačiau kol kas rodikliai ir jų ribinės vertės nėra priimtos. Daugiau informacijos pdf ataskaitoje, 39-69 psl.								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.	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 programme is adequate and sufficient enough to provide data for the description of GES.	The programme is designed to provide adeqate data on commertially exploited species. Data will provide information on the trends of state for the relevant descriptors and for some stocks there is a GES boundary for the descriptors.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats and chapter Bedömning av tillräcklighet.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats and chapter Bedömning av tillräcklighet.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats and chapter Bedömning av tillräcklighet.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats and chapter Bedömning av tillräcklighet.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats and chapter Bedömning av tillräcklighet.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats and chapter Bedömning av tillräcklighet.	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 Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	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 Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	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 Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	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 Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	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 Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	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 Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	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 Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	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 Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	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 tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	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 tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	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 tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	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 tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	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 tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	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 tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet b. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet c. See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet d. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section) e. See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats (last section)	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
Q5g - Gap-filling date for GES assessment		By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	After2020	After2020	After2020	After2020	After2020	After2020	After2020	By2014	By2014	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2014	By2014	By2014	By2014	By2014	After2020	After2020	After2020	After2020	After2020
Q5h - Plans to implement monitoring for GES assessment		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 werden Daten zur trophischen Ebene der Fische benötigt. Diese Daten werden derzeit nicht in Fischerei Surveys erhoben.	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 werden Daten zur trophischen Ebene der Fische benötigt. Diese Daten werden derzeit nicht in Fischerei Surveys erhoben.	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 werden Daten zur trophischen Ebene der Fische benötigt. Diese Daten werden derzeit nicht in Fischerei Surveys erhoben.	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 werden Daten zur trophischen Ebene der Fische benötigt. Diese Daten werden derzeit nicht in Fischerei Surveys erhoben.	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 werden Daten zur trophischen Ebene der Fische benötigt. Diese Daten werden derzeit nicht in Fischerei Surveys erhoben.	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 werden Daten zur trophischen Ebene der Fische benötigt. Diese Daten werden derzeit nicht in Fischerei Surveys erhoben.	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.	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.	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.	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.																												No immediate development needs.	No immediate development needs.	No immediate development needs.	No immediate development needs.	No immediate development needs.	No immediate development needs.	No immediate development needs.	No immediate development needs.	No immediate development needs.	No immediate development needs.	Benthic biotope monitoring will be further developed for the next monitoring cycle based on the baseline mapping.	Benthic biotope monitoring will be further developed for the next monitoring cycle based on the baseline mapping.	Benthic biotope monitoring will be further developed for the next monitoring cycle based on the baseline mapping.	Benthic biotope monitoring will be further developed for the next monitoring cycle based on the baseline mapping.	No immediate development needs.	No immediate development needs.	No immediate development needs.	No immediate development needs.	No immediate development needs.	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) working group (HELCOM FISH-PRO II) where indicators on the status of fish communities are developed, data analysis is carried out at regional level and gaps are identified. Where appropriate, consideration shall be given to shortcomings and possible solutions. For more information in the pdf report, pages 16-20.	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) working group (HELCOM FISH-PRO II) where indicators on the status of fish communities are developed, data analysis is carried out at regional level and gaps are identified. Where appropriate, consideration shall be given to shortcomings and possible solutions. For more information in the pdf report, pages 16-20.	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) working group (HELCOM FISH-PRO II) where indicators on the status of fish communities are developed, data analysis is carried out at regional level and gaps are identified. Where appropriate, consideration shall be given to shortcomings and possible solutions. For more information in the pdf report, pages 16-20.	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) working group (HELCOM FISH-PRO II) where indicators on the status of fish communities are developed, data analysis is carried out at regional level and gaps are identified. Where appropriate, consideration shall be given to shortcomings and possible solutions. For more information in the pdf report, pages 16-20.																										Filling gaps in data and assessment methods.	The programme needs additional filling of gaps in data and assessment methods.	Filling of gaps in data and assessment methods.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
Q6a -Relevant targets	Q6a - Environmental target	UZO3 UZO4	UZO3 UZO4	UZO3 UZO4	UZO3 UZO4	UZO3 UZO4	UZO3 UZO4					DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_18_BAL DK_21_BAL DK_32_BAL	DK_18_BAL DK_21_BAL DK_32_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_20_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_13_BAL DK_23_BAL DK_36_BAL	Target 01 Target 02 Target 04 Target 17 Target 30	Target 01 Target 02 Target 04 Target 17 Target 30	Target 01 Target 02 Target 04 Target 17 Target 30	Target 01 Target 02 Target 04 Target 17 Target 30	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 05 Target 13 Target 15 Target 16 Target 18	Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18	Target 01 Target 02 Target 03 Target 17 Target 30	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 06 Target 07 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26	Target 06 Target 07 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26	Target 06 Target 07 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26	Target 09 Target 19 Target 23	Target 09 Target 19 Target 23	Target 09 Target 19 Target 23	Target 09 Target 19 Target 23	Target 09 Target 19 Target 23	4	4	4	4	4	4	4	4	4	4	4	4	4	4	4	4	4	4	4	4	Target 1 Target 6	Target 1 Target 6	Target 1 Target 6	Target 1 Target 6	Target 1 Target 6	Target 1 Target 6	Target 1 Target 6												C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4							A.1	A.1	A.1	A.1	A.1	A.1	A.1	A.1	A.1	A.1	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4	C.3 C.4
Q6a -Relevant targets	Q6a - Associated indicator	UZO3_IND_3.2.3 UZO3_IND_3.3.1 UZO4_IND_4.2.1 UZO4_IND_4.3.4	UZO3_IND_3.2.3 UZO3_IND_3.3.1 UZO4_IND_4.2.1 UZO4_IND_4.3.4	UZO3_IND_3.2.3 UZO3_IND_3.3.1 UZO4_IND_4.2.1 UZO4_IND_4.3.4	UZO3_IND_3.2.3 UZO3_IND_3.3.1 UZO4_IND_4.2.1 UZO4_IND_4.3.4	UZO3_IND_3.2.3 UZO3_IND_3.3.1 UZO4_IND_4.2.1 UZO4_IND_4.3.4	UZO3_IND_3.2.3 UZO3_IND_3.3.1 UZO4_IND_4.2.1 UZO4_IND_4.3.4					DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_17_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_1_BAL DK_2_BAL DK_5_BAL DK_6_BAL DK_8_BAL DK_15_BAL DK_16_BAL DK_31_BAL	DK_18_BAL DK_21_BAL DK_32_BAL	DK_18_BAL DK_21_BAL DK_32_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_14_BAL DK_17_BAL DK_29_BAL DK_30_BAL DK_36_BAL DK_41_BAL	DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_18_BAL DK_19_BAL DK_22_BAL DK_23_BAL DK_24_BAL DK_25_BAL DK_32_BAL DK_33_BAL DK_34_BAL DK_35_BAL	DK_13_BAL DK_23_BAL DK_36_BAL	Target 01 Target 02 Target 04 Target 17 Target 30	Target 01 Target 02 Target 04 Target 17 Target 30	Target 01 Target 02 Target 04 Target 17 Target 30	Target 01 Target 02 Target 04 Target 17 Target 30	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 05 Target 13 Target 15 Target 16 Target 18	Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18	Target 01 Target 02 Target 03 Target 17 Target 30	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 06 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26	Target 06 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26	Target 06 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26	Target 09 Target 19 Target 23	Target 09 Target 19 Target 23	Target 09 Target 19 Target 23	Target 09 Target 19 Target 23	Target 09 Target 19 Target 23	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	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	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	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	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f	4.3.1 a 4.3.1 b 4.3.1 c 4.3.1 d 4.3.1 e 4.3.1 f
Q6b - Adequacy for assessment of targets	Q6b_SuitableData	N	N	N	N	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	N	Y	Y	Y	Y	Y	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y
Q6b - Adequacy for assessment of targets	Q6b_EstablishedMethods	Y	Y	Y	Y	Y	Y	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	Y	Y	N	N	Y	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y
Q6b - Adequacy for assessment of targets	Q6d_AdequateCapacity	Y	Y	Y	Y	Y	Y	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y
Q6c - Target updating		Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y								Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y
Q6d - Description of programme for targets assessment		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.	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.	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.	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.	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.	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.	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 werden kann. Darüber hinaus gibt es das UZ "Meere ohne Beeinträchtigung der marinen Arten und Lebensräume durch die Auswirkungen menschlicher Aktivitäten". Dieses UZ muss für die Anwendung auf pelagische Habitate weiter konkretisiert werden.	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 werden kann. Darüber hinaus gibt es das UZ "Meere ohne Beeinträchtigung der marinen Arten und Lebensräume durch die Auswirkungen menschlicher Aktivitäten". Dieses UZ muss für die Anwendung auf pelagische Habitate weiter konkretisiert werden.	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 werden kann. Darüber hinaus gibt es das UZ "Meere ohne Beeinträchtigung der marinen Arten und Lebensräume durch die Auswirkungen menschlicher Aktivitäten". Dieses UZ muss für die Anwendung auf pelagische Habitate weiter konkretisiert werden.	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 werden kann. Darüber hinaus gibt es das UZ "Meere ohne Beeinträchtigung der marinen Arten und Lebensräume durch die Auswirkungen menschlicher Aktivitäten". Dieses UZ muss für die Anwendung auf pelagische Habitate weiter konkretisiert werden.	The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 1 and 4. Existing data series will provide information on variability, trends and distance from levels recorded earlier and/or provide data for the assessment of possible progress towards reaching targets.	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf	Link til NOVANA + beskrivelse af supplerende overvågning + OSPAR/HELCOM. Naturstyrelsen har udarbejdet beredskabsplan for havpattedyr (rev 2012): http://www.naturstyrelsen.dk/NR/rdonlyres/E0931558-C9F1-47AB-B56C-46B6CB934CA6/139243/Beredskabsplanforhavpattedyrmarts2012.pdf Beredskabsplanen for havpattedyr skal bl.a. medvirke til overvågningen af sæler og hvalers sundhed og populationsstatus gennem registrering, obduktion og udtagning af prøver fra strandede dyr. Den seneste (2012) af de årlige rapporter om strandede havpattedyr kan findes her: http://www.fimus.dk/images/PDF/beredskabsrapport%20-%202012%20lav%20oplsning.pdf	The programme provides data on key indicators for descriptor 4. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 4. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 3. Existing data series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.	The programme provides data on keyindicators for descriptor 5. Together with existing data series information on variability, trends and distances from levels recorded previously and will provide data for assessing possible progress towards reaching targets.	The programme provides data on key indicators for descriptor 7. Togehter with existing data series information on variability, trends and distances from levels recorded previously the programme will provide data for assessing possible progress towards reaching targets.	The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)	The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)	The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)	The progress towards the 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 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 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 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 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.	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.	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.	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.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.	2015 metais numatoma patikslinti tikslus ir susijusius rodiklius. Tuomet bus vertinamas monitoringo pakankamumas ir adekvatumas vertinant tikslų pažangą bei programos trūkumų šalinimas.								Programme will deliver frequent (yearly) data on birds and assossiated attributes.	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 programme will provide sufficient data.	Programme is designed to provide frequent data on the changes in the commercialy exploited fish stocks which will enable the adequate estimation of the progress towards targets.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See Programme Pelagiska livsmiljöer, Chapter Bedömning av tillräcklighet	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
Q6e - Gap-filling date for targets assessment		By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	After2020	After2020	After2020	After2020	After2020	After2020	After2020	By2018	By2018	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2020	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2020	By2018	By2020	By2018	By2020	By2018	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014
Q6f - Plans to implement monitoring for targets assessment		Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Einige der deutschen Umweltziele setzten eine genaue Vorstellung von Zielzuständen voraus, die bisher noch nicht genauer spezifiziert sind. Dies betrifft beispielsweise die Längenstruktur in Fischbeständen oder die Abundanz von ausgewählten Fischarten. Eine nationale Abstimmung dieser Lücken wird durch die Fortschritte in den internationalen Meeresübereinkommen (HELCOM/OSPAR) erleichtert und bis 2018 erfolgen.	Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Einige der deutschen Umweltziele setzten eine genaue Vorstellung von Zielzuständen voraus, die bisher noch nicht genauer spezifiziert sind. Dies betrifft beispielsweise die Längenstruktur in Fischbeständen oder die Abundanz von ausgewählten Fischarten. Eine nationale Abstimmung dieser Lücken wird durch die Fortschritte in den internationalen Meeresübereinkommen (HELCOM/OSPAR) erleichtert und bis 2018 erfolgen.	Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Einige der deutschen Umweltziele setzten eine genaue Vorstellung von Zielzuständen voraus, die bisher noch nicht genauer spezifiziert sind. Dies betrifft beispielsweise die Längenstruktur in Fischbeständen oder die Abundanz von ausgewählten Fischarten. Eine nationale Abstimmung dieser Lücken wird durch die Fortschritte in den internationalen Meeresübereinkommen (HELCOM/OSPAR) erleichtert und bis 2018 erfolgen.	Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Einige der deutschen Umweltziele setzten eine genaue Vorstellung von Zielzuständen voraus, die bisher noch nicht genauer spezifiziert sind. Dies betrifft beispielsweise die Längenstruktur in Fischbeständen oder die Abundanz von ausgewählten Fischarten. Eine nationale Abstimmung dieser Lücken wird durch die Fortschritte in den internationalen Meeresübereinkommen (HELCOM/OSPAR) erleichtert und bis 2018 erfolgen.	Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Einige der deutschen Umweltziele setzten eine genaue Vorstellung von Zielzuständen voraus, die bisher noch nicht genauer spezifiziert sind. Dies betrifft beispielsweise die Längenstruktur in Fischbeständen oder die Abundanz von ausgewählten Fischarten. Eine nationale Abstimmung dieser Lücken wird durch die Fortschritte in den internationalen Meeresübereinkommen (HELCOM/OSPAR) erleichtert und bis 2018 erfolgen.	Das Monitoringprogramm kann eine vollständige Einschätzung zur Erreichung der Umweltziele erst dann liefern, wenn die nationalen, operativen Umweltziele entsprechend konkretisiert und quantifiziert und passende Indikatoren entwickelt wurden und anwendbar sind. Im Zusammenhang mit der Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Einige der deutschen Umweltziele setzten eine genaue Vorstellung von Zielzuständen voraus, die bisher noch nicht genauer spezifiziert sind. Dies betrifft beispielsweise die Längenstruktur in Fischbeständen oder die Abundanz von ausgewählten Fischarten. Eine nationale Abstimmung dieser Lücken wird durch die Fortschritte in den internationalen Meeresübereinkommen (HELCOM/OSPAR) erleichtert und bis 2018 erfolgen.	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 Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Siehe auch Monitoringprogramm "Eutrophierung"	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 Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Siehe auch Monitoringprogramm "Eutrophierung"	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 Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Siehe auch Monitoringprogramm "Eutrophierung"	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 Erstellung der Maßnahmenprogramme nach Art. 13 MSRL wird eine solche Konkretisierung und Quantifizierung der Umweltziele nach Art. 10 MSRL vorgenommen. Dieser Prozess wird noch bis 2018 andauern. Siehe auch Monitoringprogramm "Eutrophierung"																																				Program is fully adequate	Program is fully adequate										See 5h answer.	See 5h answer.	See 5h answer.	See 5h answer.																								Fill gaps in data and assessment methods.	Fill gaps in data and assessment methods.	Filling the gaps in data and methods		Filling gaps in data and assessment methods.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See Programme Pelagiska livsmiljöer, Chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
Q7a - Relevant activities								AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	Fisheries	Fisheries	Fisheries	Fisheries	Fisheries	Fisheries	Fisheries	CablesPipelines Dredging Fisheries LandClaimDefence MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal TourismRecreation	CablesPipelines Dredging Fisheries LandClaimDefence MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal TourismRecreation	CablesPipelines Dredging Fisheries LandClaimDefence MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal TourismRecreation	CablesPipelines Dredging Fisheries LandClaimDefence MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal TourismRecreation	CablesPipelines Dredging Fisheries LandClaimDefence MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal TourismRecreation	CablesPipelines Dredging Fisheries LandClaimDefence MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal TourismRecreation	AgricultForestry Industry Urban	AgricultForestry Industry Urban	Fisheries SeaweedOtherSeafood	Fisheries SeaweedOtherSeafood	Fisheries SeaweedOtherSeafood	Fisheries SeaweedOtherSeafood	Fisheries SeaweedOtherSeafood	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	CablesPipelines Dredging LandClaimDefence MiningSandGravel	Hunting UsesActivitiesOther	Hunting UsesActivitiesOther	Hunting UsesActivitiesOther	Hunting UsesActivitiesOther	Hunting UsesActivitiesOther						CablesPipelines Dredging MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal	CablesPipelines Dredging MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal	CablesPipelines Dredging MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal	CablesPipelines Dredging MiningSandGravel OffshoreStructures Ports RenewableEnergy Shipping SolidWasteDisposal	TourismRecreation	TourismRecreation	TourismRecreation	TourismRecreation	TourismRecreation	CablesPipelines Dredging Fisheries Ports ResearchSurvey Shipping SolidWasteDisposal	CablesPipelines Dredging Fisheries Ports ResearchSurvey Shipping SolidWasteDisposal	CablesPipelines Dredging Fisheries Ports ResearchSurvey Shipping SolidWasteDisposal	CablesPipelines Dredging Fisheries Ports ResearchSurvey Shipping SolidWasteDisposal	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	AgricultForestry Dredging Industry Ports SolidWasteDisposal Urban	Aquaculture Shipping	Aquaculture Shipping	Aquaculture Shipping	Aquaculture Shipping	Aquaculture Shipping	Aquaculture Shipping	Aquaculture Shipping	LandClaimDefence RenewableEnergy	LandClaimDefence RenewableEnergy	CablesPipelines Dredging Fisheries OffshoreStructures Ports Shipping SolidWasteDisposal StorageGases TourismRecreation	Industry	Fisheries ResearchSurvey	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry CablesPipelines Defence Dredging Fisheries Industry MiningSandGravel OffshoreStructures OilGas Ports RenewableEnergy Shipping SolidWasteDisposal Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban	AgricultForestry Fisheries Industry Urban
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.	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.	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.	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.	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.	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.	Siehe Monitoringprogramm "Eutrophierung"	Siehe Monitoringprogramm "Eutrophierung"	Siehe Monitoringprogramm "Eutrophierung"	Siehe Monitoringprogramm "Eutrophierung"	The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs	The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs	The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs	The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs	The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs	The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs	The programme provides data on key indicators in the marine environment together data data on relevant pressures impacting the biodiversity and food webs	The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.	The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.	The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.	The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.	The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.	The programme provides data on key indicators in the marine area which together with relevant data on pressures and activities may be used to identify needs for possible new measures.	The programme provide data on key indicators in the water column together with the relevant pressures impacting the biodiversity and habitat quality of the water column.	The programme provide data on key indicators in the water column together with the relevant pressures impacting the biodiversity and habitat quality of the water column.	According to guidelines of ICES agreements	According to guidelines of ICES agreements	According to guidelines of ICES agreements	According to guidelines of ICES agreements	According to guidelines of ICES agreements	Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.	Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.	Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.	Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.	Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.	Monitoring activities related to eutrophication has been performed since early 1980'ties in a high quality programme inspired by HELCOM COMBINE and OSPAR guidleines. The monitoring programme has been found to be very useful for setting up measures on the input sources. Financing could be provided following the programmes ability to document cause-effect relations.	The programme provides data on key hydrological indicators including pressures impacting the hydrological quality. Extraction of nonliving ressources is regulated in detail in Staturoy Order no. 1169 issued 3/10-2013.	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.	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.	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.	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.	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	No monitoring of activities	No monitoring of activities	No monitoring activities	No monitoring activities	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.	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.	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.	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.	The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive.	The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive.	The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive.	The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive.	The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive.	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.	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.	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.	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.	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis	Pagrindinė problema kol kas susijusi su besitęsiančia eutrofikacija, nors buveinių pokyčius gali įtakoti kiti veiksniai, sukeliantys hidrologinių sąlygų (vandens temperatūros, druskingumo) pasikeitimus. Copepoda grupės biomasė rodo zooplanktono bendrijos struktūrą ir planktofagių žuvų maistinę bazę. Zooplanktono mikrofagų biomasė indikuoja zooplanktono bendrijos struktūrą ir mažo dydžio fitoplanktono bei bakterioplanktono gausumą, kuris dažnai išauga esant eutrofikacijai. Šis rodiklis taip pat rodo planktofagių žuvų maistinę bazę. Fitoplanktono įvairovės rodiklis indikuoja eutrofikacijos procesus, kuomet didėjant maisto medžiagų koncentracijai vandenyje keičiasi fitoplanktono bendrijos sudėtis								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 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.	Pelagic habitats are reflecting human activity esspessially eutrofication and can be indicative on the changes in pressure output.	The programme is estimating the condition of commercially exploited fish in a yearly manner. The data on commertially axploited fish is collected once a year.	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)	See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See Programme Pelagiska livsmiljöer, Chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats	See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
Q7c - Relevant measures
Q7e - Adequacy for assessment of measures	Q7d - Adequate data	N	N	N	N	N	N	Y	Y	Y	Y																																															Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y								Y	Y	Y	Y	Y
Q7e - Adequacy for assessment of measures	Q7d - Established methods																																																									Y	Y	Y	Y	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N								Y	Y	N	N
Q7e - Adequacy for assessment of measures	Q7d - Adequate understanding of GES	N	N	N	N	N	N	Y	Y	Y	Y																																															Y	Y	Y	Y	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N	N								Y	Y	Y	N	Y
Q7e - Adequacy for assessment of measures	Q7d - Adequate capacity	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y																																															Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y	Y								Y	Y	Y	Y	Y
Q7e - Adequacy for assessment of measures	Q7d - Addresses activities and pressures	N	N	N	N	N	N	Y	Y	Y	Y																																															Y	Y	Y	Y																								Y	Y	Y	Y	Y
Q7e - Adequacy for assessment of measures	Q7d - Addresses effectiveness of measures	Y	Y	Y	Y	Y	Y	N	N	N	N																																															Y	Y	Y	Y																										Y	Y	Y
Q7d - Description of monitoring for measures		Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018. Das derzeitige Monitoring von Fischen basiert auf den fischereiwissenschaftlichen Surveys, welche die Erfassung von kommerziell genutzten Arten als Schwerpunkt haben. Diese Surveys sind auf die großräumige Erfassung der Abundanz und Verteilung von Fischpopulationen und -Beständen ausgelegt. Demnach kann das Monitroingprogramm großräumige Auswirkungen von Fischerei und Umweltveränderungen (Salinität, Temperatur, Sauerstoff) darstellen. Im Rahmen der MSRL sind jedoch auch kleinräumigere fischereiliche Maßnahmen (Schutzgebiete) vorgesehen. Um zu beurteilen, wie sich diese Maßnahmen auf die lokalen Fischpopulationen auswirken werden, existieren bisher keine ausreichenden Monitoringprogramme. Um den Erfolg von Schutzgebieten zu überprüfen, müssen neue Programme aufgelegt werden.	Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018. Das derzeitige Monitoring von Fischen basiert auf den fischereiwissenschaftlichen Surveys, welche die Erfassung von kommerziell genutzten Arten als Schwerpunkt haben. Diese Surveys sind auf die großräumige Erfassung der Abundanz und Verteilung von Fischpopulationen und -Beständen ausgelegt. Demnach kann das Monitroingprogramm großräumige Auswirkungen von Fischerei und Umweltveränderungen (Salinität, Temperatur, Sauerstoff) darstellen. Im Rahmen der MSRL sind jedoch auch kleinräumigere fischereiliche Maßnahmen (Schutzgebiete) vorgesehen. Um zu beurteilen, wie sich diese Maßnahmen auf die lokalen Fischpopulationen auswirken werden, existieren bisher keine ausreichenden Monitoringprogramme. Um den Erfolg von Schutzgebieten zu überprüfen, müssen neue Programme aufgelegt werden.	Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018. Das derzeitige Monitoring von Fischen basiert auf den fischereiwissenschaftlichen Surveys, welche die Erfassung von kommerziell genutzten Arten als Schwerpunkt haben. Diese Surveys sind auf die großräumige Erfassung der Abundanz und Verteilung von Fischpopulationen und -Beständen ausgelegt. Demnach kann das Monitroingprogramm großräumige Auswirkungen von Fischerei und Umweltveränderungen (Salinität, Temperatur, Sauerstoff) darstellen. Im Rahmen der MSRL sind jedoch auch kleinräumigere fischereiliche Maßnahmen (Schutzgebiete) vorgesehen. Um zu beurteilen, wie sich diese Maßnahmen auf die lokalen Fischpopulationen auswirken werden, existieren bisher keine ausreichenden Monitoringprogramme. Um den Erfolg von Schutzgebieten zu überprüfen, müssen neue Programme aufgelegt werden.	Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018. Das derzeitige Monitoring von Fischen basiert auf den fischereiwissenschaftlichen Surveys, welche die Erfassung von kommerziell genutzten Arten als Schwerpunkt haben. Diese Surveys sind auf die großräumige Erfassung der Abundanz und Verteilung von Fischpopulationen und -Beständen ausgelegt. Demnach kann das Monitroingprogramm großräumige Auswirkungen von Fischerei und Umweltveränderungen (Salinität, Temperatur, Sauerstoff) darstellen. Im Rahmen der MSRL sind jedoch auch kleinräumigere fischereiliche Maßnahmen (Schutzgebiete) vorgesehen. Um zu beurteilen, wie sich diese Maßnahmen auf die lokalen Fischpopulationen auswirken werden, existieren bisher keine ausreichenden Monitoringprogramme. Um den Erfolg von Schutzgebieten zu überprüfen, müssen neue Programme aufgelegt werden.	Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018. Das derzeitige Monitoring von Fischen basiert auf den fischereiwissenschaftlichen Surveys, welche die Erfassung von kommerziell genutzten Arten als Schwerpunkt haben. Diese Surveys sind auf die großräumige Erfassung der Abundanz und Verteilung von Fischpopulationen und -Beständen ausgelegt. Demnach kann das Monitroingprogramm großräumige Auswirkungen von Fischerei und Umweltveränderungen (Salinität, Temperatur, Sauerstoff) darstellen. Im Rahmen der MSRL sind jedoch auch kleinräumigere fischereiliche Maßnahmen (Schutzgebiete) vorgesehen. Um zu beurteilen, wie sich diese Maßnahmen auf die lokalen Fischpopulationen auswirken werden, existieren bisher keine ausreichenden Monitoringprogramme. Um den Erfolg von Schutzgebieten zu überprüfen, müssen neue Programme aufgelegt werden.	Das nationale Maßnahmenprogramm Art. 13 MSRL befindet sich derzeit noch in der Aufstellung. Aussagen, wie das Monitoring eine Effizienzkontrolle der Maßnahmen gewährleistet, können erst nach Festlegung der einzelnen Maßnahmen getroffen werden. Die Fragen 7c bis 7f können somit im ersten Berichtszyklus noch nicht vollständig beantwortet werden. Dies erfolgt im zweiten Berichtszyklus 2018. Das derzeitige Monitoring von Fischen basiert auf den fischereiwissenschaftlichen Surveys, welche die Erfassung von kommerziell genutzten Arten als Schwerpunkt haben. Diese Surveys sind auf die großräumige Erfassung der Abundanz und Verteilung von Fischpopulationen und -Beständen ausgelegt. Demnach kann das Monitroingprogramm großräumige Auswirkungen von Fischerei und Umweltveränderungen (Salinität, Temperatur, Sauerstoff) darstellen. Im Rahmen der MSRL sind jedoch auch kleinräumigere fischereiliche Maßnahmen (Schutzgebiete) vorgesehen. Um zu beurteilen, wie sich diese Maßnahmen auf die lokalen Fischpopulationen auswirken werden, existieren bisher keine ausreichenden Monitoringprogramme. Um den Erfolg von Schutzgebieten zu überprüfen, müssen neue Programme aufgelegt werden.	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. Zu jeder Maßnahme sind entsprechende Indikatoren vorgesehen, die den Erfolg der Maßnahme anzeigen. Mit dem Monitoring zu Deskriptor 5 "Eutrophierung" soll überprüft werden, ob das Maßnahmenbündel zur Reduzierung der Nährstoffeinträge und in Folge zur Reduzierung der Eutrophierung führt.	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. Zu jeder Maßnahme sind entsprechende Indikatoren vorgesehen, die den Erfolg der Maßnahme anzeigen. Mit dem Monitoring zu Deskriptor 5 "Eutrophierung" soll überprüft werden, ob das Maßnahmenbündel zur Reduzierung der Nährstoffeinträge und in Folge zur Reduzierung der Eutrophierung führt.	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. Zu jeder Maßnahme sind entsprechende Indikatoren vorgesehen, die den Erfolg der Maßnahme anzeigen. Mit dem Monitoring zu Deskriptor 5 "Eutrophierung" soll überprüft werden, ob das Maßnahmenbündel zur Reduzierung der Nährstoffeinträge und in Folge zur Reduzierung der Eutrophierung führt.	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. Zu jeder Maßnahme sind entsprechende Indikatoren vorgesehen, die den Erfolg der Maßnahme anzeigen. Mit dem Monitoring zu Deskriptor 5 "Eutrophierung" soll überprüft werden, ob das Maßnahmenbündel zur Reduzierung der Nährstoffeinträge und in Folge zur Reduzierung der Eutrophierung führt.														Subprogrammes contained in the programme enables monitoring of the land-based inputs that will make it possible to assess the effectiveness of possible measures regulating the inputs.	Subprogrammes contained in the programme enables monitoring of the land-based inputs that will make it possible to assess the effectiveness of possible measures regulating the inputs.																																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 measure and integrated impact). The adequacy of the monitoring programme will be assessed accordingly. At the same time, common measures are planned at regional level for the whole region. The proposed measures will be considered and, where appropriate, planned to be implemented.	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 measure and integrated impact). The adequacy of the monitoring programme will be assessed accordingly. At the same time, common measures are planned at regional level for the whole region. The proposed measures will be considered and, where appropriate, planned to be implemented.	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 measure and integrated impact). The adequacy of the monitoring programme will be assessed accordingly. At the same time, common measures are planned at regional level for the whole region. The proposed measures will be considered and, where appropriate, planned to be implemented.	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 measure and integrated impact). The adequacy of the monitoring programme will be assessed accordingly. At the same time, common measures are planned at regional level for the whole region. The proposed measures will be considered and, where appropriate, planned to be implemented.																								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 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	The programme is estimating the condition of commercially exploited fish in a yearly manner. The data on commertially axploited fish is collected once a year.
Q7f - Gap-filling date for activities and measures		By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	By2018	After2020	After2020	After2020	After2020	After2020	After2020	After2020	By2020	By2020	By2020	By2020	By2014	By2020	By2014	By2020	By2014	By2020	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2018	By2014	By2018	By2014	By2018	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014	By2014
Q8a - Links to existing Monitoring Programmes		CFP-DC-MAP HELCOM Habitats TWSC	CFP-DC-MAP HELCOM Habitats TWSC	CFP-DC-MAP HELCOM Habitats TWSC	CFP-DC-MAP HELCOM Habitats TWSC	CFP-DC-MAP HELCOM Habitats TWSC	CFP-DC-MAP HELCOM Habitats TWSC	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	CFP-DC-MAP HELCOM	CFP-DC-MAP HELCOM	CFP-DC-MAP HELCOM	CFP-DC-MAP HELCOM	CFP-DC-MAP HELCOM	CFP-DC-MAP HELCOM	CFP-DC-MAP HELCOM	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	HELCOM WFD	HELCOM WFD	CFP-DC-MAP	CFP-DC-MAP	CFP-DC-MAP	CFP-DC-MAP	CFP-DC-MAP	BathingWater Birds HELCOM Habitats Nitrates OSPAR UWWTD WFD	BathingWater Birds HELCOM Habitats Nitrates OSPAR UWWTD WFD	BathingWater Birds HELCOM Habitats Nitrates OSPAR UWWTD WFD	BathingWater Birds HELCOM Habitats Nitrates OSPAR UWWTD WFD	BathingWater Birds HELCOM Habitats Nitrates OSPAR UWWTD WFD	BathingWater Birds HELCOM Habitats Nitrates OSPAR UWWTD WFD	CFP-DC-MAP HELCOM Habitats WFD	Birds HELCOM Habitats	Birds HELCOM Habitats	Birds HELCOM Habitats	Birds HELCOM Habitats	Birds HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	HELCOM Habitats	HELCOM Habitats	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM Habitats WFD	BathingWater HELCOM WFD	BathingWater HELCOM WFD	BathingWater HELCOM WFD	BathingWater HELCOM WFD	BathingWater HELCOM WFD	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	Habitats	Habitats	Habitats	Habitats	Habitats	Habitats	Habitats	Birds HELCOM Habitats	Birds HELCOM Habitats	CFP-DC-MAP HELCOM	HELCOM	CFP-DC-MAP	Birds HELCOM Habitats Other The counts of wintering waterfowl are part of the international waterfowl inventories coordinated internationally by Wetlands International. The program also delivers data for the Eurasian Waterbird Agreement and thus also for the Convention on Wetlands (Ramsaar).	Birds HELCOM Habitats Other The counts of wintering waterfowl are part of the international waterfowl inventories coordinated internationally by Wetlands International. The program also delivers data for the African European Waterfowl Agreement (AEWA) and thus also for the Convention on Wetlands (Ramsaar).	Birds HELCOM Habitats Other The counts of wintering waterfowl are part of the international waterfowl inventories coordinated internationally by Wetlands International. The program also delivers data for the Eurasian Waterbird Agreement and thus also for the Convention on Wetlands (Ramsaar).	Birds HELCOM Habitats Other The counts of wintering waterfowl are part of the international waterfowl inventories coordinated internationally by Wetlands International. The program also delivers data for the African European Waterfowl Agreement (AEWA) and thus also for the Convention on Wetlands (Ramsaar).	Birds HELCOM Habitats Other The counts of wintering waterfowl are part of the international waterfowl inventories coordinated internationally by Wetlands International. The program also delivers data for the Eurasian Waterbird Agreement and thus also for the Convention on Wetlands (Ramsaar).	Birds HELCOM Habitats Other The counts of wintering waterfowl are part of the international waterfowl inventories coordinated internationally by Wetlands International. The program also delivers data for the African European Waterfowl Agreement (AEWA) and thus also for the Convention on Wetlands (Ramsaar).	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM Habitats WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	HELCOM WFD	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats	CFP-DC-MAP HELCOM Habitats
Reference sub-programme	Sub-programme ID							BALDE_Sub_087	BALDE_Sub_087	BALDE_Sub_092	BALDE_Sub_092	BALDK-D01-05_abundance_fish_coastal	BALDK-D01-07a_abund_fish_offshore_demersal	BALDK-D01-08_abundance_fish_commercial	BALDK-D01-14_population_fish_demersal	BALDK-D08-02_health_fish_demersal	BALDK-D08-03_health_fish_commercial	BALDK-D08-06_health_fish_coastal	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-D04-01_community_phytoplankton	BALDK-D04-02_community_zooplankton	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		BALFI-D01,04,06bir-1	BALFI-D01,04,06bir-2	BALFI-D01,04,06bir-3	BALFI-D01,04,06bir-4	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-D01,04,06pel-1	BALFI-D01,04,06pel-2	BALFI-D01,04,06pel-3	BALFI-D01,04,06pel-4	BALFI-D01,04,06pel-5	BALLT-D01234_FishCoastal	BALLT-D01234_FishCoastal	BALLT-D01234_FishCoastal	BALLT-D01234_FishCoastal			BALLT-D024_Zoopl	BALLT-D024_Zoopl	BALLT-D025_Phyto	BALLT-D025_Phyto	BALLT-D057_WaterPhys	BALLT-D057_WaterPhys	BALLT-D05_ChlA	BALLT-D05_ChlA	BALLT-D05_Nutrients	BALLT-D05_Nutrients	BALLT-D05_WaterChem	BALLT-D05_WaterChem	BALLT-D07_Ice	BALLT-D07_Ice								BALPL-D0104-WaterBirds	BALPL-D0104-WhiteTailedEagle	BALPL-D0104-Fish	BALPL-D0104-WaterColumnHabitats	BALPL-D03-01	BALSE-Birds-D14-Hackande	BALSE-Birds-D14-Hackande	BALSE-Birds-D14-Overvintrande	BALSE-Birds-D14-Overvintrande	BALSE-HAZ-D814-Havsorn	BALSE-HAZ-D814-Havsorn	BALSE-COMFISH-D314-Al	BALSE-COMFISH-D314-Al	BALSE-COMFISH-D314-Lax	BALSE-COMFISH-D314-Lax	BALSE-Fish-D14-Kust	BALSE-Fish-D14-Kust	BALSE-HAZ-D814-Fiskhalsa	BALSE-HAZ-D814-Fiskhalsa	BALSE-HAZ-D814-Salhalsa	BALSE-HAZ-D814-Salhalsa	BALSE-mammals-D14-Sal	BALSE-mammals-D14-Sal	BALSE-mammals-D14-Tumlare	BALSE-mammals-D14-Tumlare			BALSE-EUTRO-D514-Syre	BALSE-EUTRO-D514-Syre	BALSE-PEL-D145-Algblomning	BALSE-PEL-D145-Algblomning	BALSE-PEL-D145-Pigment	BALSE-PEL-D145-Pigment	BALSE-PEL-D145-Vaxtplankton	BALSE-PEL-D145-Vaxtplankton
Reference sub-programme	Sub-programme name	Mobile species - population characteristics	Mobile species - abundance and/or biomass	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - population characteristics	Mobile species - abundance and/or biomass	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Pelagic habitats - community characteristics	Pelagic habitats - community characteristics	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Mobile species - health status	Mobile species - health status	Mobile species - health status	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Mobile species - population characteristics	Mobile species - state of habitats	Mobile species - state of habitats	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	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	Activities extracting non-living resources (sand, gravel, dredging)	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	Mobile species - abundance and/or biomass	Plankton blooms (biomass, frequency)	Microbial pathogen levels - in water column (bathing waters)	Water column - hydrological characteristics	Water column - physical characteristics	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Water column - hydrological characteristics	Water column - hydrological characteristics	Pelagic habitats - community characteristics	Pelagic habitats - community characteristics	Pelagic habitats - community characteristics	Pelagic habitats - community characteristics	Water column - physical characteristics	Water column - physical characteristics	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Nutrient levels - in water column	Nutrient levels - in water column	Water column - chemical characteristics	Water column - chemical characteristics	Ice cover	Ice cover	Pelagic habitats - community characteristics	Plankton blooms (biomass, frequency)	Seabed habitats - community characteristics	Benthic species - abundance and/or biomass	Seabed habitats - distribution and extent	Non-indigenous species - abundance and/or biomass	Non-indigenous species inputs - from specific sources	Mobile species - population characteristics	Mobile species - population characteristics	Mobile species - population characteristics	Pelagic habitats - community characteristics	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 - 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 - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - health status	Mobile species - health status	Mobile species - health status	Mobile species - health status	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Water column - chemical characteristics	Water column - chemical characteristics	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Other	Other	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Benthic species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Benthic species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass
Q4g - Sub-programmes	Sub-programme ID							BALDE_Sub_087	BALDE_Sub_087	BALDE_Sub_092	BALDE_Sub_092	BALDK-D01-05_abundance_fish_coastal	BALDK-D01-07a_abund_fish_offshore_demersal	BALDK-D01-08_abundance_fish_commercial	BALDK-D01-14_population_fish_demersal	BALDK-D08-02_health_fish_demersal	BALDK-D08-03_health_fish_commercial	BALDK-D08-06_health_fish_coastal	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-D04-01_community_phytoplankton	BALDK-D04-02_community_zooplankton	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		BALFI-D01,04,06bir-1	BALFI-D01,04,06bir-2	BALFI-D01,04,06bir-3	BALFI-D01,04,06bir-4	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-D01,04,06pel-1	BALFI-D01,04,06pel-2	BALFI-D01,04,06pel-3	BALFI-D01,04,06pel-4	BALFI-D01,04,06pel-5	BALLT-D01234_FishCoastal	BALLT-D01234_FishCoastal	BALLT-D01234_FishCoastal	BALLT-D01234_FishCoastal			BALLT-D024_Zoopl	BALLT-D024_Zoopl	BALLT-D025_Phyto	BALLT-D025_Phyto	BALLT-D057_WaterPhys	BALLT-D057_WaterPhys	BALLT-D05_ChlA	BALLT-D05_ChlA	BALLT-D05_Nutrients	BALLT-D05_Nutrients	BALLT-D05_WaterChem	BALLT-D05_WaterChem	BALLT-D07_Ice	BALLT-D07_Ice								BALPL-D0104-WaterBirds	BALPL-D0104-WhiteTailedEagle	BALPL-D0104-Fish	BALPL-D0104-WaterColumnHabitats	BALPL-D03-01	BALSE-Birds-D14-Hackande	BALSE-Birds-D14-Hackande	BALSE-Birds-D14-Overvintrande	BALSE-Birds-D14-Overvintrande	BALSE-HAZ-D814-Havsorn	BALSE-HAZ-D814-Havsorn	BALSE-COMFISH-D314-Al	BALSE-COMFISH-D314-Al	BALSE-COMFISH-D314-Lax	BALSE-COMFISH-D314-Lax	BALSE-Fish-D14-Kust	BALSE-Fish-D14-Kust	BALSE-HAZ-D814-Fiskhalsa	BALSE-HAZ-D814-Fiskhalsa	BALSE-HAZ-D814-Salhalsa	BALSE-HAZ-D814-Salhalsa	BALSE-mammals-D14-Sal	BALSE-mammals-D14-Sal	BALSE-mammals-D14-Tumlare	BALSE-mammals-D14-Tumlare			BALSE-EUTRO-D514-Syre	BALSE-EUTRO-D514-Syre	BALSE-PEL-D145-Algblomning	BALSE-PEL-D145-Algblomning	BALSE-PEL-D145-Pigment	BALSE-PEL-D145-Pigment	BALSE-PEL-D145-Vaxtplankton	BALSE-PEL-D145-Vaxtplankton
Q4g - Sub-programmes	Sub-programme name	Mobile species - population characteristics	Mobile species - abundance and/or biomass	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - population characteristics	Mobile species - abundance and/or biomass	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Pelagic habitats - community characteristics	Pelagic habitats - community characteristics	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Mobile species - health status	Mobile species - health status	Mobile species - health status	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Mobile species - population characteristics	Mobile species - state of habitats	Mobile species - state of habitats	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	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	Activities extracting non-living resources (sand, gravel, dredging)	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	Mobile species - abundance and/or biomass	Plankton blooms (biomass, frequency)	Microbial pathogen levels - in water column (bathing waters)	Water column - hydrological characteristics	Water column - physical characteristics	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Mobile species - abundance and/or biomass	Mobile species - population characteristics	Water column - hydrological characteristics	Water column - hydrological characteristics	Pelagic habitats - community characteristics	Pelagic habitats - community characteristics	Pelagic habitats - community characteristics	Pelagic habitats - community characteristics	Water column - physical characteristics	Water column - physical characteristics	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Nutrient levels - in water column	Nutrient levels - in water column	Water column - chemical characteristics	Water column - chemical characteristics	Ice cover	Ice cover	Pelagic habitats - community characteristics	Plankton blooms (biomass, frequency)	Seabed habitats - community characteristics	Benthic species - abundance and/or biomass	Seabed habitats - distribution and extent	Non-indigenous species - abundance and/or biomass	Non-indigenous species inputs - from specific sources	Mobile species - population characteristics	Mobile species - population characteristics	Mobile species - population characteristics	Pelagic habitats - community characteristics	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 - 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 - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - health status	Mobile species - health status	Mobile species - health status	Mobile species - health status	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Water column - chemical characteristics	Water column - chemical characteristics	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Other	Other	Plankton blooms (biomass, frequency)	Plankton blooms (biomass, frequency)	Benthic species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass	Benthic species - abundance and/or biomass	Mobile species - abundance and/or biomass	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)	Mobile species - abundance and/or biomass	Mobile species - abundance and/or biomass
Q4k - Monitoring purpose								StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	Activities	StateImpact	StateImpact	Activities	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	Activities	Activities	Activities	StateImpact	Activities	Activities	StateImpact	StateImpact	StateImpact	Pressurse	Pressurse Measures		StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact Pressurse Activities	StateImpact	StateImpact	StateImpact Activities	StateImpact	StateImpact	StateImpact Pressurse Activities Measures	StateImpact Pressurse Activities Measures	StateImpact Pressurse Activities Measures	StateImpact Pressurse Activities Measures			StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact								StateImpact	StateImpact	StateImpact	StateImpact	StateImpact Pressurse Activities	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact			StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact	StateImpact
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 nationalen Monitorings bedienen somit zu großen Teilen auch die Sub-Programme des Helsinki-Übereinkommens. Diese werden im HELCOM-Monitoring-Manual (http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual) beschrieben, das sich derzeit noch in der Erstbearbeitung befindet. Nach dessen Fertigstellung sollen Verlinkungen zwischen den nationalen und den regionalen Sub-Programmen hergestellt werden. Weiterführende Informationen zum nationalen Monitoring sind in den Kennblättern Zooplankton, Phytoplankton unter http://www.blmp-online.de/Seiten/Monitoringhandbuch.htm mit dem dort angegebenen Stand zu finden. Nach einem Systemwechsel werden ab Mitte 2015 aktuelle Informationen unter http://mhb.meeresschutz.info bereitgestellt. Die berichtsrelevanten Informationen zu diesem Subprogramm Pelagische Habitate - Merkmale der Artengemeinschaften sind in aggregierter Form unter http://mhb.meeresschutz.info/de/monitoring/sub-programm/bal/87.html zu finden. Sie werden unabhängig vom Berichtszyklus fortlaufend aktuell gehalten.	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 nationalen Monitorings bedienen somit zu großen Teilen auch die Sub-Programme des Helsinki-Übereinkommens. Diese werden im HELCOM-Monitoring-Manual (http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual) beschrieben, das sich derzeit noch in der Erstbearbeitung befindet. Nach dessen Fertigstellung sollen Verlinkungen zwischen den nationalen und den regionalen Sub-Programmen hergestellt werden. Weiterführende Informationen zum nationalen Monitoring sind in den Kennblättern Zooplankton, Phytoplankton unter http://www.blmp-online.de/Seiten/Monitoringhandbuch.htm mit dem dort angegebenen Stand zu finden. Nach einem Systemwechsel werden ab Mitte 2015 aktuelle Informationen unter http://mhb.meeresschutz.info bereitgestellt. Die berichtsrelevanten Informationen zu diesem Subprogramm Pelagische Habitate - Merkmale der Artengemeinschaften sind in aggregierter Form unter http://mhb.meeresschutz.info/de/monitoring/sub-programm/bal/87.html zu finden. Sie werden unabhängig vom Berichtszyklus fortlaufend aktuell gehalten.	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 nationalen Monitorings bedienen somit zu großen Teilen auch die Sub-Programme des Helsinki-Übereinkommens. Diese werden im HELCOM-Monitoring-Manual (http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual) beschrieben, das sich derzeit noch in der Erstbearbeitung befindet. Nach dessen Fertigstellung sollen Verlinkungen zwischen den nationalen und den regionalen Sub-Programmen hergestellt werden. Weiterführende Informationen zum nationalen Monitoring sind im Kennblatt Phytoplankton unter http://www.blmp-online.de/Seiten/Monitoringhandbuch.htm mit dem dort angegebenen Stand zu finden. Nach einem Systemwechsel werden ab Mitte 2015 aktuelle Informationen unter http://mhb.meeresschutz.info bereitgestellt. Die berichtsrelevanten Informationen zu diesem Subprogramm Planktonblüten (Biomasse, Frequenz) sind in aggregierter Form unter http://mhb.meeresschutz.info/de/monitoring/sub-programm/bal/92.html zu finden. Sie werden unabhängig vom Berichtszyklus fortlaufend aktuell gehalten.	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 nationalen Monitorings bedienen somit zu großen Teilen auch die Sub-Programme des Helsinki-Übereinkommens. Diese werden im HELCOM-Monitoring-Manual (http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual) beschrieben, das sich derzeit noch in der Erstbearbeitung befindet. Nach dessen Fertigstellung sollen Verlinkungen zwischen den nationalen und den regionalen Sub-Programmen hergestellt werden. Weiterführende Informationen zum nationalen Monitoring sind im Kennblatt Phytoplankton unter http://www.blmp-online.de/Seiten/Monitoringhandbuch.htm mit dem dort angegebenen Stand zu finden. Nach einem Systemwechsel werden ab Mitte 2015 aktuelle Informationen unter http://mhb.meeresschutz.info bereitgestellt. Die berichtsrelevanten Informationen zu diesem Subprogramm Planktonblüten (Biomasse, Frequenz) sind in aggregierter Form unter http://mhb.meeresschutz.info/de/monitoring/sub-programm/bal/92.html zu finden. Sie werden unabhängig vom Berichtszyklus fortlaufend aktuell gehalten.	Catches from the recreational fisheries are registered on a voluntary basis by ”key” fishermen at fixed stations in most parts of the Danish coasts. The catches are performed with standard gillnets (one mesh size, 65 mm) and/or fyke nets, with up to 3 samples monthly in the beginning of each month, and from around April to November. Because of the mesh size used, the gillnets sample mostly adults, whereas juveniles of flounder and cod may be caught in the fyke nets. At present about 100+ fishers are invovled in the project. the last report with a detailed description can be down loaded http://orbit.dtu.dk/files/100552186/Publishers_version.pdf	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.	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 predator species sampled in the Baltic Sea are cod and whiting (in those areas where it occurs). The overall goal is to sample ten stomachs per 1 cm size group of cod and whiting from each ICES Subdivision (SDs 21 - 26 & 28) in each quarter. The ten stomachs may include empty stomachs, however, stomachs that are obviously regurgitated are discarded (see below for details on which stomachs to select). Within each SD, a wide geographical coverage of samples should be obtained whenever possible. In those SDs with many stations and where large catches can be expected (SDs 21-26 for cod and SDs 21-24 for whiting), this can be achieved by limiting the sampling frequency to (a) no more than 2 stomachs per cm group per haul, and (b) no more than 2 stomachs per cm group per day. However, in those SDs with fewer stations and/or where catches may be relatively small (SD 28 for cod and SD 25 for whiting), a higher sampling frequency per haul/day may need to be chosen in order to obtain sufficient numbers of samples per length group.	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	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.	Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.6 shows the position of the stations. 33% of the stations are in the BALDK area and 67% of the stations are in ANSDK area. Technical manual for the marine survey http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ Describe the procedure for sampling in the field and the quality control of the datasets collected. The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR.	Details can bee found in The national survey program (NOVANA): http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ Table 8.1 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.6 shows the position of the stations. 17% of the stations are in the BALDK area and 83% of the stations are in ANSDK area. Technical manual for the marine survey http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/ Describe the procedure for sampling in the field and the quality control of the datasets collected. The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR.	The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.	The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.	The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below. As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible.	Catches from the recreational fisheries are registered on a voluntary basis by ”key” fishermen at fixed stations in most parts of the Danish coasts. The catches are performed with standard gillnets (one mesh size, 65 mm) and/or fyke nets, with up to 3 samples monthly in the beginning of each month, and from around April to November. Because of the mesh size used, the gillnets sample mostly adults, whereas juveniles of flounder and cod may be caught in the fyke nets. At present about 100+ fishers are invovled in the project. the last report with a detailed description can be downloaded: http://orbit.dtu.dk/files/100552186/Publishers_version.pdf	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).		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	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: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass	This sub-programme also refers to the monitoring which has been reported under the Water Framework Directive. Further information on the sub-programme is described in: HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass	This sub-programme refers to the monitoring which has been reported under the Bathing water directive (2006/7/EU) and the Water Framework Directive. Essential information describing this national sub-programme is available at: EEA State of bathing water site: http://www.eea.europa.eu/themes/water/interactive/bathing/state-of-bathing-waters-1	This sub-programme also refers to the monitoring which has been reported under the Water Framework Directive. Further information describing this sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity	Essential information describing this sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29 HELCOM Monitoring manual - Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice	Water Framework directive, Habitats directive; Monitoring incorporated into present programme and described in Monitoring programme description, paper report.	Water Framework directive, Habitats directive; Monitoring incorporated into present programme and described in Monitoring programme description, paper report.	Water Framework directive, Habitats directive; Monitoring incorporated into present programme and described in Monitoring programme description, paper report.	Water Framework directive, Habitats directive; Monitoring incorporated into present programme and described in Monitoring programme description, paper report.			Monitoring incorporated into present programme and described in Monitoring programme paper report	Monitoring incorporated into present programme and described in Monitoring programme paper report	Water Framework Directive; Monitoring incorporated into present programme.	Water Framework Directive; Monitoring incorporated into present programme.	HELCOM monitoring manual, Water Framework Directive. Monitoring incorporated into present programme	HELCOM monitoring manual, Water Framework Directive. Monitoring incorporated into present programme	Water Framework Directive. Monitoring incorporated into present programme and described in Monitoring programme paper report	Water Framework Directive. Monitoring incorporated into present programme and described in Monitoring programme paper report	Water Framework Directive. Monitoring incorporated into present programme and described in Monitoring programme	Water Framework Directive. Monitoring incorporated into present programme and described in Monitoring programme	Water Framework Directive. Monitoring incorporated into present programme and described in Monitoring programme paper report.	Water Framework Directive. Monitoring incorporated into present programme and described in Monitoring programme paper report.	Monitoring incorporated into present programme.	Monitoring incorporated into present programme.								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.	Programme is performed as a Helcom Combine Monitoring and reflects all relevant criteria and indicators for MSFD.	http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf	"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 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 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	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	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	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"	"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	Sub-programme Health status in HELCOM Monitoring Manual	Habitats Directive Helcom monitoring manual - Sub-programme Seal abundance	Habitats Directive Helcom monitoring manual - Sub-programme Seal abundance	Habitats Directive Helcom monitoring manual - Sub-programme 3: Harbour porpoise abundance	Habitats Directive Helcom monitoring manual - Sub-programme 3: Harbour porpoise abundance			WFD monitoring programme Sub-programme O2, pH, pCO2, H2S in Helcom monitoring manual	WFD monitoring programme Sub-programme O2, pH, pCO2, H2S in Helcom monitoring manual	OSPAR JAMP theme E	OSPAR JAMP theme E	"WFD monitoring programme Helcom monitoring manual - sub-programme Pigments	"WFD monitoring programme Helcom monitoring manual - sub-programme Pigments	"WFD monitoring programme Sub-programme Species composition, abundance and biomass in HELCOM Monitoring Manual	"WFD monitoring programme Sub-programme Species composition, abundance and biomass in HELCOM Monitoring Manual
Q5c - Features	Q5c - Habitats							WaterColumnHabitatsAll	WaterColumnHabitatsAll	WaterColumnHabitatsAll	WaterColumnHabitatsAll														RedSalinity	RedSalinity	RedSalinity MarineCoast	RedSalinity MarineCoast	RedSalinity MarineCoast	RedSalinity MarineCoast	RedSalinity MarineCoast	LitSed RedSalinity	LitSed RedSalinity	LitSed RedSalinity	LitSed RedSalinity	LitSed RedSalinity	LitSed RedSalinity	LitSed RedSalinity											LitRock LitSed ShallRock ShallCoarseSed ShallSand ShallMud ShallMxdSed ShelfCoarseSed ShelfSand ShelfMud ShelfMxdSed	LitRock LitSed ShallRock ShallCoarseSed ShallSand ShallMud ShallMxdSed ShelfCoarseSed ShelfSand ShelfMud ShelfMxdSed	LitRock LitSed ShallRock ShallCoarseSed ShallSand ShallMud ShallMxdSed ShelfCoarseSed ShelfSand ShelfMud ShelfMxdSed	LitRock LitSed ShallRock ShallCoarseSed ShallSand ShallMud ShallMxdSed ShelfCoarseSed ShelfSand ShelfMud ShelfMxdSed	RedSalinity VarSalinity MarineCoast MarineShelf IceHabitat	RedSalinity VarSalinity MarineCoast MarineShelf IceHabitat	RedSalinity VarSalinity MarineCoast MarineShelf IceHabitat	RedSalinity VarSalinity MarineCoast MarineShelf IceHabitat	RedSalinity VarSalinity MarineCoast MarineShelf IceHabitat	VarSalinity MarineCoast	VarSalinity MarineCoast	VarSalinity MarineCoast	VarSalinity MarineCoast	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	VarSalinity MarineCoast MarineShelf	ShallRock ShallMud ShelfMud VarSalinity MarineCoast MarineShelf	ShallRock ShallMud ShelfMud VarSalinity MarineCoast MarineShelf	ShallRock ShallMud ShelfMud VarSalinity MarineCoast MarineShelf	ShallRock ShallMud ShelfMud VarSalinity MarineCoast MarineShelf	ShallRock ShallMud ShelfMud VarSalinity MarineCoast MarineShelf	ShallRock ShallMud ShelfMud VarSalinity MarineCoast MarineShelf	ShallRock ShallMud ShelfMud VarSalinity MarineCoast MarineShelf	WaterColumnHabitatsAll	WaterColumnHabitatsAll	ShelfSand RedSalinity VarSalinity MarineCoast	RedSalinity VarSalinity MarineCoast MarineShelf	ShelfSand ShelfMud RedSalinity VarSalinity MarineCoast MarineShelf																					RedSalinity	RedSalinity	RedSalinity	RedSalinity	RedSalinity	RedSalinity	RedSalinity	RedSalinity	RedSalinity	RedSalinity
Q5c - Features	Q5c - Species list	All caught fish species Anguilla_anguilla_Linnaeus_1785 Clupea_harengus_Linnaeus_1758 Coregonus_spp FishAll FishCoastal FishDemersal FishDiadromous FishPelagic FunctionalGroupOther Gadus_morhua_Linnaeus_1758 Limanda_limanda_Linnaeus_1758 Merlangius_merlangus_Linnaeus_1758 Platichthys_flesus_Linnaeus_1758 Pleuronectes_platessa_Linnaeus_1758 Salmo_trutta_trutta_Linnaeus_1758 Scophthalmus_maximus_Linnaeus_1758 Scophthalmus_rhombus_Linnaeus_1758 Solea_solea_Linnaeus_1758 Sprattus_sprattus_Linnaeus_1758	All caught fish species Anguilla_anguilla_Linnaeus_1785 Clupea_harengus_Linnaeus_1758 Coregonus_spp FishAll FishCoastal FishDemersal FishDiadromous FishPelagic FunctionalGroupOther Gadus_morhua_Linnaeus_1758 Limanda_limanda_Linnaeus_1758 Merlangius_merlangus_Linnaeus_1758 Platichthys_flesus_Linnaeus_1758 Pleuronectes_platessa_Linnaeus_1758 Salmo_trutta_trutta_Linnaeus_1758 Scophthalmus_maximus_Linnaeus_1758 Scophthalmus_rhombus_Linnaeus_1758 Solea_solea_Linnaeus_1758 Sprattus_sprattus_Linnaeus_1758	All caught fish species Anguilla_anguilla_Linnaeus_1785 Clupea_harengus_Linnaeus_1758 Coregonus_spp FishAll FishCoastal FishDemersal FishDiadromous FishPelagic FunctionalGroupOther Gadus_morhua_Linnaeus_1758 Limanda_limanda_Linnaeus_1758 Merlangius_merlangus_Linnaeus_1758 Platichthys_flesus_Linnaeus_1758 Pleuronectes_platessa_Linnaeus_1758 Salmo_trutta_trutta_Linnaeus_1758 Scophthalmus_maximus_Linnaeus_1758 Scophthalmus_rhombus_Linnaeus_1758 Solea_solea_Linnaeus_1758 Sprattus_sprattus_Linnaeus_1758	All caught fish species Anguilla_anguilla_Linnaeus_1785 Clupea_harengus_Linnaeus_1758 Coregonus_spp FishAll FishCoastal FishDemersal FishDiadromous FishPelagic FunctionalGroupOther Gadus_morhua_Linnaeus_1758 Limanda_limanda_Linnaeus_1758 Merlangius_merlangus_Linnaeus_1758 Platichthys_flesus_Linnaeus_1758 Pleuronectes_platessa_Linnaeus_1758 Salmo_trutta_trutta_Linnaeus_1758 Scophthalmus_maximus_Linnaeus_1758 Scophthalmus_rhombus_Linnaeus_1758 Solea_solea_Linnaeus_1758 Sprattus_sprattus_Linnaeus_1758	All caught fish species Anguilla_anguilla_Linnaeus_1785 Clupea_harengus_Linnaeus_1758 Coregonus_spp FishAll FishCoastal FishDemersal FishDiadromous FishPelagic FunctionalGroupOther Gadus_morhua_Linnaeus_1758 Limanda_limanda_Linnaeus_1758 Merlangius_merlangus_Linnaeus_1758 Platichthys_flesus_Linnaeus_1758 Pleuronectes_platessa_Linnaeus_1758 Salmo_trutta_trutta_Linnaeus_1758 Scophthalmus_maximus_Linnaeus_1758 Scophthalmus_rhombus_Linnaeus_1758 Solea_solea_Linnaeus_1758 Sprattus_sprattus_Linnaeus_1758	All caught fish species Anguilla_anguilla_Linnaeus_1785 Clupea_harengus_Linnaeus_1758 Coregonus_spp FishAll FishCoastal FishDemersal FishDiadromous FishPelagic FunctionalGroupOther Gadus_morhua_Linnaeus_1758 Limanda_limanda_Linnaeus_1758 Merlangius_merlangus_Linnaeus_1758 Platichthys_flesus_Linnaeus_1758 Pleuronectes_platessa_Linnaeus_1758 Salmo_trutta_trutta_Linnaeus_1758 Scophthalmus_maximus_Linnaeus_1758 Scophthalmus_rhombus_Linnaeus_1758 Solea_solea_Linnaeus_1758 Sprattus_sprattus_Linnaeus_1758	FunctionalGroupOther Phyto- und Zooplanktonarten	FunctionalGroupOther Phyto- und Zooplanktonarten	FunctionalGroupOther Phyto- und Zooplanktonarten	FunctionalGroupOther Phyto- und Zooplanktonarten	CephalopodsCoastShelf FishAll FishCoastal FishDemersal FishDemersalElasmobranchs FishDiadromous FishPelagic FishPelagicElasmobranchs	CephalopodsCoastShelf FishAll FishCoastal FishDemersal FishDemersalElasmobranchs FishDiadromous FishPelagic FishPelagicElasmobranchs	CephalopodsCoastShelf FishAll FishCoastal FishDemersal FishDemersalElasmobranchs FishDiadromous FishPelagic FishPelagicElasmobranchs	CephalopodsCoastShelf FishAll FishCoastal FishDemersal FishDemersalElasmobranchs FishDiadromous FishPelagic FishPelagicElasmobranchs	CephalopodsCoastShelf FishAll FishCoastal FishDemersal FishDemersalElasmobranchs FishDiadromous FishPelagic FishPelagicElasmobranchs	CephalopodsCoastShelf FishAll FishCoastal FishDemersal FishDemersalElasmobranchs FishDiadromous FishPelagic FishPelagicElasmobranchs	CephalopodsCoastShelf FishAll FishCoastal FishDemersal FishDemersalElasmobranchs FishDiadromous FishPelagic FishPelagicElasmobranchs	AnnexII_IV_V_Species MammalsAll MammalsSeals MammalsToothedWhales	AnnexII_IV_V_Species MammalsAll MammalsSeals MammalsToothedWhales	AnnexII_IV_V_Species MammalsAll MammalsSeals MammalsToothedWhales	AnnexII_IV_V_Species MammalsAll MammalsSeals MammalsToothedWhales	AnnexII_IV_V_Species MammalsAll MammalsSeals MammalsToothedWhales	AnnexII_IV_V_Species MammalsAll MammalsSeals MammalsToothedWhales	MammalsAll	MammalsAll	CephalopodsAll FishAll FishCoastal FishDemersal FishDiadromous FishPelagic	CephalopodsAll FishAll FishCoastal FishDemersal FishDiadromous FishPelagic	CephalopodsAll FishAll FishCoastal FishDemersal FishDiadromous FishPelagic	CephalopodsAll FishAll FishCoastal FishDemersal FishDiadromous FishPelagic	CephalopodsAll FishAll FishCoastal FishDemersal FishDiadromous FishPelagic							MammalsToothedWhales	AnnexII_IV_V_Species BirdsInshoreBenthic BirdsInshoreHerbiv BirdsInshorePelagic BirdsInshoreSurface BirdsIntertidalBenthic BirdsOffshorePelagic MammalsIce MammalsSeals WildBirdSpecies	AnnexII_IV_V_Species BirdsInshoreBenthic BirdsInshoreHerbiv BirdsInshorePelagic BirdsInshoreSurface BirdsIntertidalBenthic BirdsOffshorePelagic MammalsIce MammalsSeals WildBirdSpecies	AnnexII_IV_V_Species BirdsInshoreBenthic BirdsInshoreHerbiv BirdsInshorePelagic BirdsInshoreSurface BirdsIntertidalBenthic BirdsOffshorePelagic MammalsIce MammalsSeals WildBirdSpecies	AnnexII_IV_V_Species BirdsInshoreBenthic BirdsInshoreHerbiv BirdsInshorePelagic BirdsInshoreSurface BirdsIntertidalBenthic BirdsOffshorePelagic MammalsIce MammalsSeals WildBirdSpecies	AnnexII_IV_V_Species BirdsInshoreBenthic BirdsInshoreHerbiv BirdsInshorePelagic BirdsInshoreSurface BirdsIntertidalBenthic BirdsOffshorePelagic MammalsIce MammalsSeals WildBirdSpecies	AnnexII_IV_V_Species FishCoastal FishDemersal FishDiadromous FishPelagic	AnnexII_IV_V_Species FishCoastal FishDemersal FishDiadromous FishPelagic	AnnexII_IV_V_Species FishCoastal FishDemersal FishDiadromous FishPelagic	AnnexII_IV_V_Species MammalsIce MammalsSeals MammalsToothedWhales	AnnexII_IV_V_Species MammalsIce MammalsSeals MammalsToothedWhales										AnnexII_IV_V_Species FishAll FishCoastal FishDemersal FishPelagic	AnnexII_IV_V_Species FishAll FishCoastal FishDemersal FishPelagic	AnnexII_IV_V_Species FishAll FishCoastal FishDemersal FishPelagic	AnnexII_IV_V_Species FishAll FishCoastal FishDemersal FishPelagic	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FunctionalGroupOther Phytoplankton, Zooplankton, Bacterioplankton, physical-chemical parameters	FishDemersal FishPelagic FunctionalGroupOther Zoobentoss, Zooplanktons	FishDemersal FishPelagic FunctionalGroupOther Zoobentoss, Zooplanktons	FishDemersal FishPelagic FunctionalGroupOther Zoobentoss, Zooplanktons	FishDemersal FishPelagic FunctionalGroupOther Zoobentoss, Zooplanktons	FishDemersal FishPelagic FunctionalGroupOther Zoobentoss, Zooplanktons	FishDemersal FishPelagic FunctionalGroupOther Zoobentoss, Zooplanktons	FishDemersal FishPelagic FunctionalGroupOther Zoobentoss, Zooplanktons	BirdsAll BirdsInshoreBenthic BirdsInshorePelagic BirdsInshoreSurface WildBirdSpecies	BirdsAll BirdsInshoreBenthic BirdsInshorePelagic BirdsInshoreSurface WildBirdSpecies	FishAll FishCoastal FishDemersal FishDiadromous FishPelagic	AnnexII_IV_V_Species	FishAll FishCoastal FishDemersal FishDiadromous FishPelagic	BirdsAll	BirdsAll	BirdsAll	BirdsAll	BirdsAll	BirdsAll	FishCoastal FishDiadromous	FishCoastal FishDiadromous	FishCoastal FishDiadromous	FishCoastal FishDiadromous	FishCoastal FishDiadromous	FishCoastal FishDiadromous	FishCoastal FishDiadromous	FishCoastal FishDiadromous	MammalsAll MammalsIce MammalsSeals MammalsToothedWhales	MammalsAll MammalsIce MammalsSeals MammalsToothedWhales	MammalsAll MammalsIce MammalsSeals MammalsToothedWhales	MammalsAll MammalsIce MammalsSeals MammalsToothedWhales	MammalsAll MammalsIce MammalsSeals MammalsToothedWhales	MammalsAll MammalsIce MammalsSeals MammalsToothedWhales
Q5c - Features	Q5c - Physical/Chemical features							NutrientLevels OxygenLevels Salinity SeaSurfaceTemperature Transparency pH	NutrientLevels OxygenLevels Salinity SeaSurfaceTemperature Transparency pH	NutrientLevels OxygenLevels Salinity SeaSurfaceTemperature Transparency pH	NutrientLevels OxygenLevels Salinity SeaSurfaceTemperature Transparency pH														NutrientLevels Salinity Transparency Turbidity	NutrientLevels Salinity Transparency Turbidity	Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency	Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency	Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency	Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency	Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity pH	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity pH	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity pH	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity pH	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity pH	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity pH	TopographyBathymetry											H2S, sediment color, substrate type OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature WaveExposure	H2S, sediment color, substrate type OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature WaveExposure	H2S, sediment color, substrate type OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature WaveExposure	H2S, sediment color, substrate type OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature WaveExposure	CurrentVelocity IceCover Mixing OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity Upwelling pH water level, wave height	CurrentVelocity IceCover Mixing OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity Upwelling pH water level, wave height	CurrentVelocity IceCover Mixing OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity Upwelling pH water level, wave height	CurrentVelocity IceCover Mixing OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity Upwelling pH water level, wave height	CurrentVelocity IceCover Mixing OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency Turbidity Upwelling pH water level, wave height	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency	CurrentVelocity NutrientLevels OxygenLevels Salinity SeaBottomTemperature SeaSurfaceTemperature Transparency	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH	CurrentVelocity IceCover NutrientLevels OxygenLevels PhysicalChemicalOther Salinity SeaBottomTemperature SeaSurfaceTemperature TopographyBathymetry Transparency Turbidity WaveExposure pH										OxygenLevels Salinity SeaBottomTemperature TopographyBathymetry	Mixing Salinity SeaBottomTemperature SeaSurfaceTemperature	OxygenLevels Salinity SeaBottomTemperature TopographyBathymetry
Q5c - Features	Q5c - Pressures							InputOrganics IntroNIS NutrientOrgEnrich	InputOrganics IntroNIS NutrientOrgEnrich	InputOrganics IntroNIS NutrientOrgEnrich	InputOrganics IntroNIS NutrientOrgEnrich	ExtractSpeciesFishShellfish	ExtractSpeciesFishShellfish	ExtractSpeciesFishShellfish	ExtractSpeciesFishShellfish	ExtractSpeciesFishShellfish	ExtractSpeciesFishShellfish	ExtractSpeciesFishShellfish	AcutePollutionEvents ExtractSpeciesFishShellfish Noise PhysDisturbance	AcutePollutionEvents ExtractSpeciesFishShellfish Noise PhysDisturbance	AcutePollutionEvents ExtractSpeciesFishShellfish Noise PhysDisturbance	AcutePollutionEvents ExtractSpeciesFishShellfish Noise PhysDisturbance	AcutePollutionEvents ExtractSpeciesFishShellfish Noise PhysDisturbance	AcutePollutionEvents ExtractSpeciesFishShellfish Noise PhysDisturbance	NutrientOrgEnrich	NutrientOrgEnrich	ExtractSpeciesFishShellfish Litter	ExtractSpeciesFishShellfish Litter	ExtractSpeciesFishShellfish Litter	ExtractSpeciesFishShellfish Litter	ExtractSpeciesFishShellfish Litter	NutrientOrgEnrich	NutrientOrgEnrich	NutrientOrgEnrich	NutrientOrgEnrich	NutrientOrgEnrich	NutrientOrgEnrich	PhysDam_extraction	ExtractSpeciesOther hunting of seals and seabirds	ExtractSpeciesOther hunting of seals and seabirds	ExtractSpeciesOther hunting of seals and seabirds	ExtractSpeciesOther hunting of seals and seabirds	ExtractSpeciesOther hunting of seals and seabirds				Bycatch PressureOther	Bycatch PressureOther	PhysDam PhysDam_abrasion PhysDam_extraction PhysDam_silt PhysDisturbance PhysLoss PhysLoss_Seal PhysLoss_Smother	PhysDam PhysDam_abrasion PhysDam_extraction PhysDam_silt PhysDisturbance PhysLoss PhysLoss_Seal PhysLoss_Smother	PhysDam PhysDam_abrasion PhysDam_extraction PhysDam_silt PhysDisturbance PhysLoss PhysLoss_Seal PhysLoss_Smother	PhysDam PhysDam_abrasion PhysDam_extraction PhysDam_silt PhysDisturbance PhysLoss PhysLoss_Seal PhysLoss_Smother						AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal ExtractSpeciesAll ExtractSpeciesFishShellfish InputN_Psubst IntroHazSubstOther IntroNIS NutrientOrgEnrich PhysDam_silt PhysLoss_Smother	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal ExtractSpeciesAll ExtractSpeciesFishShellfish InputN_Psubst IntroHazSubstOther IntroNIS NutrientOrgEnrich PhysDam_silt PhysLoss_Smother	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal ExtractSpeciesAll ExtractSpeciesFishShellfish InputN_Psubst IntroHazSubstOther IntroNIS NutrientOrgEnrich PhysDam_silt PhysLoss_Smother	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal ExtractSpeciesAll ExtractSpeciesFishShellfish InputN_Psubst IntroHazSubstOther IntroNIS NutrientOrgEnrich PhysDam_silt PhysLoss_Smother	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	AcutePollutionEvents BioDisturb_other ChangeHydrology ChangeSalinity ChangeThermal InputOrganics IntroNIS NutrientOrgEnrich PhysDisturbance	BioDisturb_other IntroNIS	BioDisturb_other IntroNIS	BioDisturb_other IntroNIS	BioDisturb_other IntroNIS	BioDisturb_other IntroNIS	BioDisturb_other IntroNIS	BioDisturb_other IntroNIS	AcutePollutionEvents IntroHazSubstOther IntroRadioNuclides IntroSynthComp Litter	AcutePollutionEvents IntroHazSubstOther IntroRadioNuclides IntroSynthComp Litter	AcutePollutionEvents BioDisturb_other ChangeSalinity ExtractSpeciesAll ExtractSpeciesFishShellfish IntroSynthComp Litter Noise	ChangeSalinity ChangeThermal InputN_Psubst InputOrganics NutrientOrgEnrich	AcutePollutionEvents BioDisturb_other ChangeSalinity ChangeThermal ExtractSpeciesAll ExtractSpeciesFishShellfish IntroHazSubstOther IntroRadioNuclides IntroSynthComp Litter Noise																					IntroNIS	IntroNIS	IntroNIS	IntroNIS	IntroNIS	IntroNIS	IntroNIS	IntroNIS	IntroNIS	IntroNIS	ExtractSpeciesAll	ExtractSpeciesAll	ExtractSpeciesAll	ExtractSpeciesAll	ExtractSpeciesAll	ExtractSpeciesAll	ExtractSpeciesAll	ExtractSpeciesAll	ExtractSpeciesAll	ExtractSpeciesAll
Q9a - Elements								\|\| Das Subprogramm besteht aus den/dem folgenden Messprogramm/en (=MP): MP_037 (Zooplankton (Ostsee)) und MP_041 (Phytoplankton – Artenzusammensetzung, Abundanz, Biomasse (Ostsee)) \|\| \|\| MP_037 \|\| Zooplankton \|\| MP_041 \|\| Phytoplankton	\|\| Das Subprogramm besteht aus den/dem folgenden Messprogramm/en (=MP): MP_037 (Zooplankton (Ostsee)) und MP_041 (Phytoplankton – Artenzusammensetzung, Abundanz, Biomasse (Ostsee)) \|\| \|\| MP_037 \|\| Zooplankton \|\| MP_041 \|\| Phytoplankton	\|\| Das Subprogramm besteht aus den/dem folgenden Messprogramm/en (=MP): MP_039 (Phytoplankton – Chlorophyll a und Blüten (Ostsee)) \|\| \|\| MP_039 \|\| Phytoplankton	\|\| Das Subprogramm besteht aus den/dem folgenden Messprogramm/en (=MP): MP_039 (Phytoplankton – Chlorophyll a und Blüten (Ostsee)) \|\| \|\| MP_039 \|\| Phytoplankton	Most frequently occurring species in the combined database are flounder (Platichtys flesus), eel (Anguilla anguilla), eel-pout (Zoarces viviparus) and cod (Gadus morhua).	In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information with depth, temperature, oxygen, salinity etc. is recorded.	In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.	Stomachs should be selected randomly within each length group. To assure random selection within size classes, and as additional single-fish data are needed anyways, it is recommended to use fish selected for single-fish data, otolith and maturity sampling whenever possible. The samples should be frozen individually in plastic bags including a label describing the sampled fish . Every fish needs to have a unique ID number, which is noted on the label and which makes it possible to connect the stomach to the other relevant single-fish, haul and environmental (CTD) data. Stomachs are collected from cod/whiting > = 15 cm. To ease the handling, cod and whiting < 15 cm are frozen as a whole (2 specimen per cm group and per haul).	In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information with depth, temperature, oxygen, salinity etc. is recorded.	In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.	Biological effects of contaminants: PAH-specific effects (CYP1A/EROD, PAH bile metabolites), reprodutive success in eelpout (reproductive impact, malformations).	Trend in abundance at all localities and reproductive rates at selected localities.	Trend in abundance.	Trends in population abundance.	Population trend in abundance.		Seasonal trend in density/abundance.			In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.	In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.	In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.	Most frequently occurring species in the combined database are flounder (Platichtys flesus), eel (Anguilla anguilla), eel-pout (Zoarces viviparus) and cod (Gadus morhua).	In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specific to species or species group counted and weighted and station information on depth, gear and fishing pattern is recorded. The target fish species are all commercial species.	Pressures.The data to be monitored in the current program are: Intestinal enterococci and E. coli.	ctd, fluorescens, light attenuation and oxygen	nutrients		Load of Nutrients (nitrogen and phosphorus) and water from land-based sources to marine and coastal waters.	Eutrphying inorganic nitrogen and phosphrous.		marine breeding birds	marine birds	Marine birds	Haliaetus_albicilla_Linnaeus_1758	Haliaetus_albicilla_Linnaeus_1758	Coregonus_lavaretus_Linnaeus_1758 Diadromous fish	Salmo_trutta_trutta_Linnaeus_1758	coastal fish	Halichoerus_grypus_Fabricius_1791 Phocoena_phocoena_Linnaeus_1758 Pusa_hispida_bottnica_Schreber_1775	marine seals	littoral sediment macrozoobenthos shelf sublittoral coarse sediment shelf sublittoral mixed sediment shelf sublittoral mud shelf sublittoral sand	littoral sediment macrozoobenthos shallow sublittoral coarse sediment shallow sublittoral mixed sediment shallow sublittoral mud shallow sublittoral sand	Blue mussel Littoral rock and biogenic reef Macroalgae Macrozoobenthos Shallow sublittoral rock and biogenic reef	contaminant levels in dredged material disposal of dredged matter dredging marine constructions selective exploitation of the seabed shipping	macrozooplankton	phytoplankton	Biological disturbance Introduction of microbial pathogens	physical characteristics	ice physical characteristics	Coastal fish (all species)	Coastal fish (all species)	Coastal fish (all species)	Coastal fish (all species)			zooplankton (all species)	zooplankton (all species)	phytoplankton (all species)	phytoplankton (all species)	currents sea level waves	currents sea level waves	Phytoplankton	Phytoplankton	nutrients	nutrients	biochemical oxygen consumption dissolved oxygen hydrogen sulphide pH	biochemical oxygen consumption dissolved oxygen hydrogen sulphide pH	Ice	Ice								Waterbirds in breeding season Waterbirds in wintering season	White-tailed eagle (Haliaeetus albicilla)	Coastal fish:Perca fluviatilis, Zoarces viviparus, Gadus morhua, Sander lucioperca, Rutilus rutilus, Platichthys flesus, Psetta maxima Offshore fish:Gadus morhua, Platichthys flesus, Salmo salar, Clupea harengus	Phytoplankton Zooplankton	Cod (Gadus morhua) European flounder (Platichthys flesus) Herring (Clupea harengus) Sprat (Sprattus sprattus)	"Swans. Mute swan.Ducks. F.e. Common eider, Goldeneye, Gadwall.Geese. F.e Greylag goose.Grebes. F.e. Great crested grebe.Waders. Redshank, Eurasian oystercatcher, Common ringed plover.Gulls. F.e. Herring and Lesser black-backed gull, Little gull.Terns. F.e. Arctic and Common tern.Great cormorant.Auks. F.e. Razorbill.	"Swans. Mute swan.Ducks. F.e. Common eider, Goldeneye, Gadwall.Geese. F.e Greylag goose.Grebes. F.e. Great crested grebe.Waders. Redshank, Eurasian oystercatcher, Common ringed plover.Gulls. F.e. Herring and Lesser black-backed gull, Little gull.Terns. F.e. Arctic and Common tern.Great cormorant.Auks. F.e. Razorbill.	Ducks. F.e. mallard, goldeneye, common eider.Scoters. Common and Velvet scoterGrebes. F.e. Great crested grebe.Swans. Mute and Whooper swan.Divers. F.e. Black-throated diver.Grey heron.Great cormorant.Auks. Common guillemot.	Ducks. F.e. mallard, goldeneye, common eider.Scoters. Common and Velvet scoterGrebes. F.e. Great crested grebe.Swans. Mute and Whooper swan.Divers. F.e. Black-throated diver.Grey heron.Great cormorant.Auks. Common guillemot.	Impact on white-tailed eagle reproduction	Impact on white-tailed eagle reproduction	European eel (Anguilla anguilla)	European eel (Anguilla anguilla)	Salmon (Salmo salar) and sea-trout (Salmo trutta)	Salmon (Salmo salar) and sea-trout (Salmo trutta)	All occurring species are noted. Focal species are perch and othe warm water species	All occurring species are noted. Focal species are perch and othe warm water species	Biological effect monitoring of fish (perch)	Biological effect monitoring of fish (perch)	Effects on seal reproduction.	Effects on seal reproduction.	Harbor seal, ringed seal and grey seal	Harbor seal, ringed seal and grey seal	Harbour porpoise	Harbour porpoise			Oxygen and hydrogen sulfide	Oxygen and hydrogen sulfide	Harmfull Algal Blooms	Harmfull Algal Blooms	Chlorophyll a	Chlorophyll a	Phytoplankton species, pelagic bacteria and primary production	Phytoplankton species, pelagic bacteria and primary production
Q5a - GES criteria	Relevant GES criteria	1.2 1.3 4.1 4.2 4.3	1.2 1.3 4.1 4.2 4.3	1.2 1.3 4.1 4.2 4.3	1.2 1.3 4.1 4.2 4.3	1.2 1.3 4.1 4.2 4.3	1.2 1.3 4.1 4.2 4.3	1.2 1.6 4.3 5.2	1.2 1.6 4.3 5.2	1.2 1.6 4.3 5.2	1.2 1.6 4.3 5.2	4.2	4.2	4.2	4.2	4.2	4.2	4.2	1.1 1.2 1.3 1.4 1.5 4.3	1.1 1.2 1.3 1.4 1.5 4.3	1.1 1.2 1.3 1.4 1.5 4.3	1.1 1.2 1.3 1.4 1.5 4.3	1.1 1.2 1.3 1.4 1.5 4.3	1.1 1.2 1.3 1.4 1.5 4.3	4.3	4.3	1.1 1.2 1.3 3.1 3.2 3.3 4.2	1.1 1.2 1.3 3.1 3.2 3.3 4.2	1.1 1.2 1.3 3.1 3.2 3.3 4.2	1.1 1.2 1.3 3.1 3.2 3.3 4.2	1.1 1.2 1.3 3.1 3.2 3.3 4.2	1.1 4.3 5.1 5.2 5.3	1.1 4.3 5.1 5.2 5.3	1.1 4.3 5.1 5.2 5.3	1.1 4.3 5.1 5.2 5.3	1.1 4.3 5.1 5.2 5.3	1.1 4.3 5.1 5.2 5.3	1.6 3.1 4.3 7.1 7.2	1.1 1.2 1.3 4.1 4.2 4.3 8.2	1.1 1.2 1.3 4.1 4.2 4.3 8.2	1.1 1.2 1.3 4.1 4.2 4.3 8.2	1.1 1.2 1.3 4.1 4.2 4.3 8.2	1.1 1.2 1.3 4.1 4.2 4.3 8.2	1.2 1.3 3.2 3.3 4.3	1.2 1.3 3.2 3.3 4.3	1.2 1.3 3.2 3.3 4.3	1.1 1.2 1.3 4.1 4.2 4.3 8.2	1.1 1.2 1.3 4.1 4.2 4.3 8.2	1.1 1.2 1.3 1.4 1.5 1.6 4.3 5.3 6.1 6.2	1.1 1.2 1.3 1.4 1.5 1.6 4.3 5.3 6.1 6.2	1.1 1.2 1.3 1.4 1.5 1.6 4.3 5.3 6.1 6.2	1.1 1.2 1.3 1.4 1.5 1.6 4.3 5.3 6.1 6.2	1.4 1.5 1.6 1.7 4.3 5.2	1.4 1.5 1.6 1.7 4.3 5.2	1.4 1.5 1.6 1.7 4.3 5.2	1.4 1.5 1.6 1.7 4.3 5.2	1.4 1.5 1.6 1.7 4.3 5.2	1.1 1.2 1.3 1.6 1.7 4.2	1.1 1.2 1.3 1.6 1.7 4.2	1.1 1.2 1.3 1.6 1.7 4.2	1.1 1.2 1.3 1.6 1.7 4.2	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	4.3 5.1 5.2 5.3	1.1 1.2 1.4 1.5 1.6 1.7 2.1 2.2 3.1 3.2 3.3 4.1 4.3 5.2 6.1 6.2 7.2	1.1 1.2 1.4 1.5 1.6 1.7 2.1 2.2 3.1 3.2 3.3 4.1 4.3 5.2 6.1 6.2 7.2	1.1 1.2 1.4 1.5 1.6 1.7 2.1 2.2 3.1 3.2 3.3 4.1 4.3 5.2 6.1 6.2 7.2	1.1 1.2 1.4 1.5 1.6 1.7 2.1 2.2 3.1 3.2 3.3 4.1 4.3 5.2 6.1 6.2 7.2	1.1 1.2 1.4 1.5 1.6 1.7 2.1 2.2 3.1 3.2 3.3 4.1 4.3 5.2 6.1 6.2 7.2	1.1 1.2 1.4 1.5 1.6 1.7 2.1 2.2 3.1 3.2 3.3 4.1 4.3 5.2 6.1 6.2 7.2	1.1 1.2 1.4 1.5 1.6 1.7 2.1 2.2 3.1 3.2 3.3 4.1 4.3 5.2 6.1 6.2 7.2	1.1 1.2 1.3 4.1	1.1 1.2 1.3 4.1	1.1 1.2 1.3 4.1 4.2 4.3	1.2 1.3 4.3 5.2	3.1 3.2 3.3 4.1 4.2 4.3	1.1 1.2 1.3 4.1 4.3 8.2	1.1 1.2 4.1 4.3 8.2	1.1 1.2 1.3 4.1 4.3 8.2	1.1 1.2 4.1 4.3 8.2	1.1 1.2 1.3 4.1 4.3 8.2	1.1 1.2 4.1 4.3 8.2	1.1 1.2 1.3 1.6 1.7 4.2 4.3	1.1 1.2 1.3 1.6 1.7 4.2 4.3	1.1 1.2 1.3 1.6 1.7 4.2 4.3	1.1 1.2 1.3 1.6 1.7 4.2 4.3	1.1 1.2 1.3 1.6 1.7 4.2 4.3	1.1 1.2 1.3 1.6 1.7 4.2 4.3	1.1 1.2 1.3 1.6 1.7 4.2 4.3	1.1 1.2 1.3 1.6 1.7 4.2 4.3	1.1 1.2 1.3 4.1 8.2	1.1 1.2 1.3 4.1 8.2	1.1 1.2 1.3 4.1 8.2	1.1 1.2 1.3 4.1 8.2	1.1 1.2 1.3 4.1 8.2	1.1 1.2 1.3 4.1 8.2	1.6 1.7 4.3	1.6 1.7 4.3	1.6 1.7 4.3	1.6 1.7 4.3	1.6 1.7 4.3	1.6 1.7 4.3	1.6 1.7 4.3	1.6 1.7 4.3	1.6 1.7 4.3	1.6 1.7 4.3	1.2 1.3 1.6 1.7 3.1 3.2 3.3 4.2 4.3	1.2 1.3 1.6 1.7 3.1 3.2 3.3 4.2 4.3	1.2 1.3 1.6 1.7 3.1 3.2 3.3 4.2 4.3	1.2 1.3 1.6 1.7 3.1 3.2 3.3 4.2 4.3	1.2 1.3 1.6 1.7 3.1 3.2 3.3 4.2 4.3	1.2 1.3 1.6 1.7 3.1 3.2 4.2 4.3	1.2 1.3 1.6 1.7 3.1 3.2 4.2 4.3	1.2 1.3 1.6 1.7 3.1 3.2 4.2 4.3	1.2 1.3 1.6 1.7 3.1 3.2 4.2 4.3	1.2 1.3 1.6 1.7 3.1 3.2 4.2 4.3
Q5b - GES indicators	Relevant GES indicators	1.2.1 1.3.1 4.1.1 4.2.1 4.3.1	1.2.1 1.3.1 4.1.1 4.2.1 4.3.1	1.2.1 1.3.1 4.1.1 4.2.1 4.3.1	1.2.1 1.3.1 4.1.1 4.2.1 4.3.1	1.2.1 1.3.1 4.1.1 4.2.1 4.3.1	1.2.1 1.3.1 4.1.1 4.2.1 4.3.1	1.2.1 1.6.2 4.3.1 5.2.4	1.2.1 1.6.2 4.3.1 5.2.4	1.2.1 1.6.2 4.3.1 5.2.4	1.2.1 1.6.2 4.3.1 5.2.4	4.2.1	4.2.1	4.2.1	4.2.1	4.2.1	4.2.1	4.2.1	1.1.1 1.1.2 1.2.1 1.3.1 1.4.1 1.5.1 4.3.1	1.1.1 1.1.2 1.2.1 1.3.1 1.4.1 1.5.1 4.3.1	1.1.1 1.1.2 1.2.1 1.3.1 1.4.1 1.5.1 4.3.1	1.1.1 1.1.2 1.2.1 1.3.1 1.4.1 1.5.1 4.3.1	1.1.1 1.1.2 1.2.1 1.3.1 1.4.1 1.5.1 4.3.1	1.1.1 1.1.2 1.2.1 1.3.1 1.4.1 1.5.1 4.3.1	4.3.1 5.1.1 5.2.1 5.2.2 8.1.1	4.3.1 5.1.1 5.2.1 5.2.2 8.1.1	3.1.1 3.1.2 3.2.1 3.2.2 3.3.1 4.2.1	3.1.1 3.1.2 3.2.1 3.2.2 3.3.1 4.2.1	3.1.1 3.1.2 3.2.1 3.2.2 3.3.1 4.2.1	3.1.1 3.1.2 3.2.1 3.2.2 3.3.1 4.2.1	3.1.1 3.1.2 3.2.1 3.2.2 3.3.1 4.2.1	5.1.1 5.2.1 5.2.2 5.2.3 5.2.4 5.3.1 5.3.2	5.1.1 5.2.1 5.2.2 5.2.3 5.2.4 5.3.1 5.3.2	5.1.1 5.2.1 5.2.2 5.2.3 5.2.4 5.3.1 5.3.2	5.1.1 5.2.1 5.2.2 5.2.3 5.2.4 5.3.1 5.3.2	5.1.1 5.2.1 5.2.2 5.2.3 5.2.4 5.3.1 5.3.2	5.1.1 5.2.1 5.2.2 5.2.3 5.2.4 5.3.1 5.3.2	1.6.3 6.2.1 6.2.2 7.1.1 7.2.1 7.2.2	1.1.1 1.1.2 1.2.1 4.1.1 4.3.1 8.2.1	1.1.1 1.1.2 1.2.1 4.1.1 4.3.1 8.2.1	1.1.1 1.1.2 1.2.1 4.1.1 4.3.1 8.2.1	1.1.1 1.1.2 1.2.1 4.1.1 4.3.1 8.2.1	1.1.1 1.1.2 1.2.1 4.1.1 4.3.1 8.2.1	1.2.1 1.3.1 3.1.2 3.2.2 3.3.1 3.3.2 3.3.4 4.3.1	1.2.1 1.3.1 3.1.2 3.2.2 3.3.1 3.3.2 3.3.4 4.3.1	1.2.1 1.3.1 3.1.2 3.2.2 3.3.1 3.3.2 3.3.4 4.3.1	1.1.1 1.1.2 1.2.1 1.3.1 4.1.1 4.3.1 8.2.1	1.1.1 1.1.2 1.2.1 1.3.1 4.1.1 4.3.1 8.2.1	1.4.1 1.4.2 1.5.1 1.5.2 1.6.1 1.6.2 1.6.3 4.3.1 5.3.1 6.1.1 6.1.2 6.2.2 6.2.3	1.4.1 1.4.2 1.5.1 1.5.2 1.6.1 1.6.2 1.6.3 4.3.1 5.3.1 6.1.1 6.1.2 6.2.2 6.2.3	1.4.1 1.4.2 1.5.1 1.5.2 1.6.1 1.6.2 1.6.3 4.3.1 5.3.1 6.1.1 6.1.2 6.2.2 6.2.3	1.4.1 1.4.2 1.5.1 1.5.2 1.6.1 1.6.2 1.6.3 4.3.1 5.3.1 6.1.1 6.1.2 6.2.2 6.2.3	1.4.1 1.4.2 1.5.1 1.5.2 1.6.1 1.6.2 1.6.3 1.7.1 4.3.1 5.2.2 5.2.4	1.4.1 1.4.2 1.5.1 1.5.2 1.6.1 1.6.2 1.6.3 1.7.1 4.3.1 5.2.2 5.2.4	1.4.1 1.4.2 1.5.1 1.5.2 1.6.1 1.6.2 1.6.3 1.7.1 4.3.1 5.2.2 5.2.4	1.4.1 1.4.2 1.5.1 1.5.2 1.6.1 1.6.2 1.6.3 1.7.1 4.3.1 5.2.2 5.2.4	1.4.1 1.4.2 1.5.1 1.5.2 1.6.1 1.6.2 1.6.3 1.7.1 4.3.1 5.2.2 5.2.4	1.1.1 1.2.1 1.3.1 1.6.1 1.7.1 4.2.1	1.1.1 1.2.1 1.3.1 1.6.1 1.7.1 4.2.1	1.1.1 1.2.1 1.3.1 1.6.1 1.7.1 4.2.1	1.1.1 1.2.1 1.3.1 1.6.1 1.7.1 4.2.1	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	4.3.1 5.1.1 5.1.2 5.2.1 5.2.2 5.3.2	1.6.1 1.6.2 2.2.2 5.2.4 6.1.2	1.6.1 1.6.2 2.2.2 5.2.4 6.1.2	1.6.1 1.6.2 2.2.2 5.2.4 6.1.2	1.6.1 1.6.2 2.2.2 5.2.4 6.1.2	1.6.1 1.6.2 2.2.2 5.2.4 6.1.2	1.6.1 1.6.2 2.2.2 5.2.4 6.1.2	1.6.1 1.6.2 2.2.2 5.2.4 6.1.2	1.1.1 1.1.2 4.1.1	1.1.1 1.1.2 4.1.1	1.2.1 1.3.1 1.4.2 4.1.1 4.2.1 4.3.1	1.2.1 1.6.1 1.7.1 4.3.1 5.2.4	2.1.1 3.1.1 3.1.2 3.2.1 3.2.2 3.3.1 3.3.2 3.3.3 3.3.4	1.1.1 1.2.1 1.3.1 4.1.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.5.2 1.6.1 1.6.2 1.7.1 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.5.2 1.6.1 1.6.2 1.7.1 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.5.2 1.6.1 1.6.2 1.7.1 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.5.2 1.6.1 1.6.2 1.7.1 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.5.2 1.6.1 1.6.2 1.7.1 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.5.2 1.6.1 1.6.2 1.7.1 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.5.2 1.6.1 1.6.2 1.7.1 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.5.2 1.6.1 1.6.2 1.7.1 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 4.1.1 See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.5.2 1.6.2 1.7.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer	1.1.1 1.2.1 1.3.1 1.6.1 1.6.2 1.7.1 3.1.1 3.1.2 3.2.1 3.3.1 3.3.2 3.3.3 3.3.4 4.2.1 4.3.1 GESOther See bilaga 5 Indikatorer
Q9b - Parameters monitored (state/impact)	Species distribution							MP-9b-1-1-1	MP-9b-1-1-1			MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1			MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1		MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1				MP-9b-1-1-1				MP-9b-1-1-1	MP-9b-1-1-1					MP-9b-1-1-1		MP-9b-1-1-1						MP-9b-1-1-1	MP-9b-1-1-1																															MP-9b-1-1-1 MP-9b-1-1-2	MP-9b-1-1-1	MP-9b-1-1-1																			MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1	MP-9b-1-1-1					MP-9b-1-1-1	MP-9b-1-1-1
Q9b - Parameters monitored (state/impact)	Species population size							MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2		MP-9b-1-2-1 MP-9b-1-2-2		MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2			MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1		MP-9b-1-2-1 MP-9b-1-2-2									MP-9b-1-2-1 MP-9b-1-2-2				MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1											MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2			MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2																		MP-9b-1-2-1		MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1									MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1 MP-9b-1-2-2	MP-9b-1-2-1 MP-9b-1-2-2					MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1	MP-9b-1-2-1
Q9b - Parameters monitored (state/impact)	Species population characteristics												MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3 MP-9b-1-3-6	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3	MP-9b-1-3-2 MP-9b-1-3-3 MP-9b-1-3-6	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3 MP-9b-1-3-6	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3		MP-9b-1-3-6		MP-9b-1-3-6		MP-9b-1-3-6				MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3		MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3										MP-9b-1-3-8	MP-9b-1-3-5 MP-9b-1-3-6 MP-9b-1-3-7 MP-9b-1-3-8	MP-9b-1-3-5 MP-9b-1-3-6 MP-9b-1-3-7 MP-9b-1-3-8	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-5	MP-9b-1-3-1 MP-9b-1-3-5		MP-9b-1-3-5 MP-9b-1-3-6 MP-9b-1-3-7	MP-9b-1-3-2 MP-9b-1-3-3 MP-9b-1-3-6 MP-9b-1-3-7										MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-3																								MP-9b-1-3-6	MP-9b-1-3-6	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-4 MP-9b-1-3-5	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-5	MP-9b-1-3-1 MP-9b-1-3-2 MP-9b-1-3-4 MP-9b-1-3-5 MP-9b-1-3-8					MP-9b-1-3-6	MP-9b-1-3-6	MP-9b-1-3-1 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-3	MP-9b-1-3-1 MP-9b-1-3-3
Q9b - Parameters monitored (state/impact)	Species impacts											MP-9b-1-4-1 MP-9b-1-4-3		MP-9b-1-4-1 MP-9b-1-4-2 MP-9b-1-4-3			MP-9b-1-4-1 MP-9b-1-4-2 MP-9b-1-4-3										MP-9b-1-4-1 MP-9b-1-4-2 MP-9b-1-4-3	MP-9b-1-4-1 MP-9b-1-4-2 MP-9b-1-4-3	MP-9b-1-4-1 MP-9b-1-4-2 MP-9b-1-4-3	MP-9b-1-4-1 MP-9b-1-4-3	MP-9b-1-4-1 MP-9b-1-4-2 MP-9b-1-4-3										MP-9b-1-4-4																																																							MP-9b-1-4-1	MP-9b-1-4-1	MP-9b-1-4-1	MP-9b-1-4-1
Q9b - Parameters monitored (state/impact)	Habitat distribution							MP-9b-1-5-1	MP-9b-1-5-1																																								MP-9b-1-5-1	MP-9b-1-5-1	MP-9b-1-5-1																																		MP-9b-1-5-1
Q9b - Parameters monitored (state/impact)	Habitat extent																																																MP-9b-1-6-1	MP-9b-1-6-1	MP-9b-1-6-1
Q9b - Parameters monitored (state/impact)	Habitat condition (physical-chemical)							MP-9b-1-7-1 MP-9b-1-7-2 MP-9b-1-7-6 MP-9b-1-7-8	MP-9b-1-7-1 MP-9b-1-7-2 MP-9b-1-7-6 MP-9b-1-7-8	MP-9b-1-7-1 MP-9b-1-7-2 MP-9b-1-7-4 MP-9b-1-7-6 MP-9b-1-7-8	MP-9b-1-7-1 MP-9b-1-7-2 MP-9b-1-7-4 MP-9b-1-7-6 MP-9b-1-7-8	MP-9b-1-7-1	MP-9b-1-7-1 MP-9b-1-7-11 MP-9b-1-7-2 MP-9b-1-7-6	MP-9b-1-7-11	MP-9b-1-7-1 MP-9b-1-7-11 MP-9b-1-7-2 MP-9b-1-7-6	MP-9b-1-7-1 MP-9b-1-7-11 MP-9b-1-7-2 MP-9b-1-7-6	MP-9b-1-7-11										MP-9b-1-7-11	MP-9b-1-7-11	MP-9b-1-7-11	MP-9b-1-7-1	MP-9b-1-7-11		MP-9b-1-7-1 MP-9b-1-7-2 MP-9b-1-7-6 MP-9b-1-7-7																MP-9b-1-7-12 MP-9b-1-7-13 MP-9b-1-7-6	MP-9b-1-7-12 MP-9b-1-7-13 MP-9b-1-7-6	MP-9b-1-7-12 MP-9b-1-7-13 MP-9b-1-7-5	MP-9b-1-7-12				MP-9b-1-7-1 MP-9b-1-7-13 MP-9b-1-7-2 MP-9b-1-7-7	MP-9b-1-7-13 MP-9b-1-7-3 MP-9b-1-7-4 MP-9b-1-7-5											MP-9b-1-7-3 MP-9b-1-7-4 MP-9b-1-7-5	MP-9b-1-7-3 MP-9b-1-7-4 MP-9b-1-7-5					MP-9b-1-7-6 MP-9b-1-7-8	MP-9b-1-7-6 MP-9b-1-7-8	MP-9b-1-7-13	MP-9b-1-7-13																																			MP-9b-1-7-6	MP-9b-1-7-6
Q9b - Parameters monitored (state/impact)	Habitat condition (biological)							MP-9b-1-8-1 MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-1 MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-3 MP-9b-1-8-4	MP-9b-1-8-3 MP-9b-1-8-4	MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-2 MP-9b-1-8-3										MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-2 MP-9b-1-8-3																		MP-9b-1-8-1 MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-1 MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-1 MP-9b-1-8-2 MP-9b-1-8-5 MP-9b-1-8-6		MP-9b-1-8-1 MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-1 MP-9b-1-8-2 MP-9b-1-8-3																MP-9b-1-8-4	MP-9b-1-8-4																	MP-9b-1-8-2 MP-9b-1-8-3		MP-9b-1-8-2	MP-9b-1-8-2	MP-9b-1-8-2	MP-9b-1-8-2			MP-9b-1-8-3	MP-9b-1-8-3																	MP-9b-1-8-2 MP-9b-1-8-3 MP-9b-1-8-4	MP-9b-1-8-2 MP-9b-1-8-3 MP-9b-1-8-4	MP-9b-1-8-4	MP-9b-1-8-4	MP-9b-1-8-1 MP-9b-1-8-2 MP-9b-1-8-3	MP-9b-1-8-1 MP-9b-1-8-2 MP-9b-1-8-3
Q9b - Parameters monitored (state/impact)	Habitat impacts													MP-9b-1-9-2			MP-9b-1-9-2										MP-9b-1-9-2	MP-9b-1-9-2	MP-9b-1-9-2		MP-9b-1-9-2																																																																							MP-9b-1-9-1	MP-9b-1-9-1	MP-9b-1-9-1	MP-9b-1-9-1
Q9b - Parameters monitored (pressures)	Pressure input																																			MP-9b-2-1-2	MP-9b-2-1-1															MP-9b-2-1-3
Q9b - Parameters monitored (pressures)	Pressure output							MP-9b-2-2-5	MP-9b-2-2-5				MP-9b-2-2-7		MP-9b-2-2-2 MP-9b-2-2-7	MP-9b-2-2-2 MP-9b-2-2-7		MP-9b-2-2-2														MP-9b-2-2-3		MP-9b-2-2-3		MP-9b-2-2-1																MP-9b-2-2-4			MP-9b-2-2-6																	MP-9b-2-2-3	MP-9b-2-2-3
Q9b - Parameters monitored (activity)	Activity													MP-9b-3-1-1 MP-9b-3-1-4			MP-9b-3-1-1 MP-9b-3-1-4										MP-9b-3-1-1 MP-9b-3-1-4	MP-9b-3-1-1 MP-9b-3-1-4	MP-9b-3-1-1 MP-9b-3-1-4		MP-9b-3-1-1 MP-9b-3-1-4																					MP-9b-3-1-4
Q9b Parameters monitored (other)	Other									MP-9b-4-1-1	MP-9b-4-1-1				MP-9b-4-1-1	MP-9b-4-1-1		MP-9b-4-1-1																																																																												MP-9b-4-1-1	MP-9b-4-1-1			MP-9b-4-1-1	MP-9b-4-1-1							MP-9b-4-1-1	MP-9b-4-1-1	MP-9b-4-1-1	MP-9b-4-1-1									MP-9b-4-1-1	MP-9b-4-1-1
Q41 Spatial scope								EEZ TerritorialWaters WFD_CW	EEZ TerritorialWaters WFD_CW	EEZ TerritorialWaters WFD_CW	EEZ TerritorialWaters WFD_CW	WFD_CW	EEZ BeyondMSwaters	WFD_CW EEZ BeyondMSwaters	EEZ BeyondMSwaters	EEZ BeyondMSwaters	WFD_CW EEZ BeyondMSwaters	WFD_CW	MSland_FW	WFD_CW TerritorialWaters EEZ	MSland_FW	WFD_TW WFD_CW TerritorialWaters	MSland_FW	WFD_CW TerritorialWaters	WFD_CW TerritorialWaters EEZ	WFD_CW	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		WFD_CW	WFD_CW TerritorialWaters	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	TerritorialWaters EEZ BeyondMSwaters	TerritorialWaters EEZ BeyondMSwaters	WFD_CW	WFD_CW TerritorialWaters EEZ BeyondMSwaters	WFD_CW TerritorialWaters EEZ BeyondMSwaters	WFD_TW WFD_CW	WFD_TW WFD_CW	WFD_TW WFD_CW	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	TerritorialWaters EEZ	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_CW TerritorialWaters EEZ	WFD_TW WFD_CW TerritorialWaters EEZ	WFD_CW TerritorialWaters EEZ	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_CW TerritorialWaters EEZ	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW	WFD_CW TerritorialWaters EEZ BeyondMSwaters	WFD_CW TerritorialWaters EEZ BeyondMSwaters			WFD_CW TerritorialWaters EEZ BeyondMSwaters	WFD_CW TerritorialWaters EEZ BeyondMSwaters	WFD_TW WFD_CW TerritorialWaters EEZ BeyondMSwaters	WFD_TW WFD_CW TerritorialWaters EEZ BeyondMSwaters	WFD_CW TerritorialWaters	WFD_CW TerritorialWaters	WFD_CW TerritorialWaters	WFD_CW TerritorialWaters
Q4j - Description of spatial scope								keine Angabe vorhanden!!	keine Angabe vorhanden!!	Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO (Bund/Länder-Messprogramm / Bund/Länder-Ausschuss Nord- und Ostsee)	Gemäß Verpflichtungen WRRL, MSRL, HELCOM, BLMP/BLANO (Bund/Länder-Messprogramm / Bund/Länder-Ausschuss Nord- und Ostsee)	the programme aims at determining the abundance and diversity of fish in coastal areas.	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.	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	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.	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 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/	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.		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	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: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass	HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass	Monitoring is done only on public bathing sites along the Finnish coast. One of the main sources of pathogens are the public bathing sites.	HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity	HELCOM Monitoring manual - Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29 HELCOM Monitoring manual - Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice	Monitoring is carried out in accordance to the HELCOM methods, described in Monitoring programme description, paper report, 16-17 pages	Monitoring is carried out in accordance to the HELCOM methods, described in Monitoring programme description, paper report, 16-17 pages	Monitoring is carried out in accordance to the HELCOM methods, described in Monitoring programme description, paper report, 16-17 pages	Monitoring is carried out in accordance to the HELCOM methods, described in Monitoring programme description, paper report, 16-17 pages			Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual), described in Monitoring programme paper report, 38-43 pages	Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual), described in Monitoring programme paper report, 38-43 pages	Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out over the entire sea area, at coastal stations and also is based on research ship cruises	Monitoring is carried out over the entire sea area, at coastal stations and also is based on research ship cruises	Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual), described in Monitoring programme paper report, 52-57 pages	Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual), described in Monitoring programme paper report, 52-57 pages	Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual), described in Monitoring programme description, paper report, 44-51 pages	Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual), described in Monitoring programme description, paper report, 44-51 pages	Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual), described in Monitoring programme paper report, 44-52 pages	Monitoring is carried out in all coastal water bodies and off-shore areas (coordinated within HELCOM; see HELCOM Monitoring Manual; http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual), described in Monitoring programme paper report, 44-52 pages	visual monitoring	visual monitoring								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 programme is designed to reflect the state of water column habitats and is following recommendations of the HELCOM monitoring guidelines.	The data for the programme will be available from BITS surveys	See sub-programme Häckande sjöfågel, chapter Rumslig och tidsmässig täckning	See sub-programme Häckande sjöfågel, chapter Rumslig och tidsmässig täckning	See sub-programme Övervintrande 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, chapter Rumslig och tidssmässig täckning	See sub-programme Migrerande fiskarter - ål, chapter Rumslig och tidsmässig täckning	See sub-programme Migrerande fiskarter - ål, chapter Rumslig och tidsmässig täckning	See sub-programme Migrerande fiskarter - lax, chapter Rumslig och tidsmässig täckning	See sub-programme Migrerande fiskarter - lax, chapter Rumslig och tidsmässig täckning	See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning	See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning	See sub-programme Hälsotillstånd hos kustfisk, chapter Rumslig och tidsmässig täckning	See sub-programme Hälsotillstånd hos kustfisk, chapter Rumslig och tidsmässig täckning	Se sub-programme Hälsotillstånd hos säl, chapter Rumslig och tidsmässig täckning	Se sub-programme Hälsotillstånd hos säl, chapter Rumslig och tidsmässig täckning	See sub-programme Bestånd av säl, chapter Rumslig och tidsmässig täckning	See sub-programme Bestånd av säl, chapter Rumslig och tidsmässig täckning	See sub-programme Bestånd av tumlare, chapter Rumslig och tidsmässig täckning	See sub-programme Bestånd av tumlare, chapter Rumslig och tidsmässig täckning			See sub-programme Pelagialens egenskaper - Syrekoncentration, chapter Rumslig och tidsmässig täckning	See sub-programme Pelagialens egenskaper - Syrekoncentration, chapter Rumslig och tidsmässig täckning	See sub-programme Skadliga algblomningar, chapter Rumslig och tidsmässig täckning	See sub-programme Skadliga algblomningar, chapter Rumslig och tidsmässig täckning	See sub-programme Växyplankton - Pigment, chapter Rumslig och tidsmässig täckning	See sub-programme Växyplankton - Pigment, chapter Rumslig och tidsmässig täckning	See sub-programme Växtplankton och pelagiska bakterier, chapter Rumslig och tidsmässig täckning	See sub-programme Växtplankton och pelagiska bakterier, chapter Rumslig och tidsmässig täckning
Marine Unit IDs		DE_BAL	DE_BAL	DE_BAL	DE_BAL	DE_BAL	DE_BAL	DE_BAL	DE_BAL	DE_BAL	DE_BAL	BALDK	BALDK	BALDK	BALDK	BALDK	BALDK	BALDK	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL_DK_RG_001	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-FI-RG-Baltic Sea	BAL-LT-AA-01	BAL-LT-AA-01	BAL-LT-AA-01	BAL-LT-AA-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LT-MS-01	BAL-LV-SD-006	BAL-LV-SD-006	BAL-LV-SD-006	BAL-LV-SD-006	BAL-LV-SD-006	BAL-LV-SD-006	BAL-LV-SD-006	BAL-PL-AA-24 BAL-PL-AA-28 BAL-PL-AA-BB BAL-PL-AA-TWIWB1 BAL-PL-AA-TWIWB8	BAL-PL-AA-24 BAL-PL-AA-28 BAL-PL-AA-BB BAL-PL-AA-TWIWB1 BAL-PL-AA-TWIWB8	BAL-PL-AA-24 BAL-PL-AA-26 BAL-PL-AA-28 BAL-PL-AA-BB BAL-PL-AA-EGB BAL-PL-AA-GB BAL-PL-AA-TWIWB1 BAL-PL-AA-TWIWB8	BAL-PL-AA-24 BAL-PL-AA-26 BAL-PL-AA-28 BAL-PL-AA-BB BAL-PL-AA-EGB BAL-PL-AA-GB BAL-PL-AA-TWIWB1 BAL-PL-AA-TWIWB8	BAL-PL-AA-28 BAL-PL-AA-EGB	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	ANS-SE-SR-Nordsjon	ANS-SE-SR-Nordsjon	ANS-SE-SR-Nordsjon	ANS-SE-SR-Nordsjon	ANS-SE-SR-Nordsjon	ANS-SE-SR-Nordsjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon	BAL-SE-RG-Ostersjon
Q4h - Temporal scope	Start date- End date	-	-	-	-	-	-	1979-9999	1979-9999	1979-9999	1979-9999	2005-9999	1991-9999	1995-9999	1991-9999	1991-9999	1995-9999	2004-9999	1979-9999	2011-9999	1979-9999	2011-9999	1979-9999	2011-9999	1987-9999	1990-9999	1995-9999	1995-9999	1995-9999	2005-9999	1995-9999	1975-9999	1987-9999	1987-9999	1987-9999	1989-9999	1989-9999	-	1948-9999	1965-9999	1986-9999	1970-9999	1970-9999	1980-9999	1976-9999	1970-9999	1988-9999	1977-9999	1965-9999	1965-9999	2006-9999	2014-9999	1976-9999	1979-9999	2009-9999	1979-9999	1791-9999	1992-9999	1992-9999	1992-9999	1992-9999	-	-	1990-9999	1990-9999	1980-9999	1980-9999	1980-9999	1980-9999	1980-9999	1980-9999	1972-9999	1972-9999	1972-9999	1972-9999	1980-9999	1980-9999	-	-	-	-	-	-	-	2011-9999	2015-9999	2014-9999	1999-9999	2014-9999	2010-9999	2010-9999	1967-9999	1967-9999	1965-9999	1965-9999	2004-9999	2004-9999	2004-9999	2004-9999	1960-9999	1960-9999	1988-9999	1988-9999	1977-9999	1977-9999	1975-9999	1975-9999	2011-9999	2011-9999	-	-	1902-9999	1902-9999	2002-9999	2002-9999	1982-9999	1982-9999	1983-9999	1983-9999	-	-	-	-	-	-	-	-	-	-
Q9h - Temporal resolution of sampling								\|\| MP_037 \|\| 5 mal pro Jahr \|\| MP_041 \|\| Beim Monitoring der offenen See (BSH-finanziert, hauptsächlich Bereich der AWZ) 5 Seereisen pro Jahr. Monitoring der Küstengewässer MV: März bis Oktober, monatlich. Monitoring der Küstengewässer SH: monatlich bis 2monatlich Other	\|\| MP_037 \|\| 5 mal pro Jahr \|\| MP_041 \|\| Beim Monitoring der offenen See (BSH-finanziert, hauptsächlich Bereich der AWZ) 5 Seereisen pro Jahr. Monitoring der Küstengewässer MV: März bis Oktober, monatlich. Monitoring der Küstengewässer SH: monatlich bis 2monatlich Other	\|\| MP_039 \|\| Beim Monitoring der offenen See (BSH-finanziert, hauptsächlich Bereich der AWZ) 5 Seereisen pro Jahr. Monitoring der Küstengewässer MV: März bis Oktober, monatlich. Monitoring der Küstengewässer SH: monatlich bis 2monatlich. Other	\|\| MP_039 \|\| Beim Monitoring der offenen See (BSH-finanziert, hauptsächlich Bereich der AWZ) 5 Seereisen pro Jahr. Monitoring der Küstengewässer MV: März bis Oktober, monatlich. Monitoring der Küstengewässer SH: monatlich bis 2monatlich. Other	Monthly	6monthly	Continually	6monthly	6monthly	Continually	Yearly	Yearly	6yearly	Yearly	6yearly	Yearly	Yearly	Yearly	Yearly	Continually	Continually	Continually	Monthly	Continually	Yearly	Monthly	Monthly	Monthly	Yearly	Continually		Yearly	Yearly	Asneeded	Yearly	Yearly	2-3 times per spawning season Other	Yearly	Yearly	Yearly	Unknown	Yearly	Yearly	Yearly	6yearly	Yearly	Yearly	4 times per year Other	3monthly	3yearly	3yearly Yearly monitoring is planning	3yearly Yearly monitoring is planning	3yearly Yearly monitoring is planning	3yearly Yearly monitoring is planning			Yearly	Yearly	Yearly 3monthly Monthly	Yearly 3monthly Monthly	Yearly Continually	Yearly Continually	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly								Yearly	Yearly 3monthly	Yearly	5 times a year Other	Yearly Unknown	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Other two or three times a year for silver eel (blankål)	Other two or three times a year for silver eel (blankål)	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Frequency depends on found and reported dead seals, as well as hunted seals. Hence it varies. Other	Frequency depends on found and reported dead seals, as well as hunted seals. Hence it varies. Other	Yearly	Yearly	Other irregularly (2011, 2013)	Other irregularly (2011, 2013)			Monthly - 2-weekly Other	Monthly - 2-weekly Other	Other Remote sensing: Daily during 3 months Sampling of harmful algae species - Monthly	Other Remote sensing: Daily during 3 months Sampling of harmful algae species - Monthly	6-monthly - 2-weekly	6-monthly - 2-weekly	Yearly - 2-weekly Other	Yearly - 2-weekly Other
Q9c - Monitoring method								\|\| 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_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_039 \|\| HELCOM COMBINE manual http://www.helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual	In this project 102 voluntary recreational fishermen participated, using either gillnets, fyke-nets or both gear types. Note that the results resented in this report represent catches reported by recreational fishermen. All species have caught have been registered and length measurements have been taken. The results showed a high fish biodiversity in Danish coastal waters. A total of 49 fish species were registered in gillnets and 72 in fyke-nets. This projec represent the largest and longest time series on catches in gillnets and fyke-nets along the Danish coasts.	ICES methods. http://www.ices.dk/marine-data/Documents/DATRAS%20Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf.	ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea.	In a food web content stomach data is colleted on a regular basis from 2008 from the Baltic sea cod. The stomach data are collected an analysed according to the:	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	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	http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_5_fytoplankton.pdf	http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_6_Mikrozooplankton.pdf http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_7_Mesozooplankton.pdf	ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.	ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.	ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state. Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks.	In this project 102 voluntary recreational fishermen participated, using either gillnets, fyke-nets or both gear types. Note that the results resented in this report represent catches reported by recreational fishermen. All species have caught have been registered and length measurements have been taken. The results showed a high fish biodiversity in Danish coastal waters. A total of 49 fish species were registered in gillnets and 72 in fyke-nets. This projec represent the largest and longest time series on catches in gillnets and fyke-nets along the Danish coasts. As age and length and weight by age are followed on a regular basis it is possible to follow the development over time, to estimate if the population is in a healthy state.	ICES methods 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.		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	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: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass	HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass	National Supervisory Authority for Welfare and Health - http://www.valvira.fi/files/ohjeet/Yleisten_uimarantojen_uimaveden_valvonta.pdf (in Finnish)	HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity	HELCOM Monitoring manual - Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29 HELCOM Monitoring manual - Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice	Method described in Monitoring programme, text-based paper report.	Method described in Monitoring programme, text-based paper report.	Method described in Monitoring programme, text-based paper report.	Method described in Monitoring programme, text-based paper report.			Monitoring is carried out according to the HELCOM guidelines	Monitoring is carried out according to the HELCOM guidelines	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)	Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual)								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://www.helcom.fi/action-areas/monitoring-and-assessment/manuals-and-guidelines/combine-manual	http://cdr.eionet.europa.eu/pl/eu/msfd_mp/msfd4text/envvypola/Program_monitoringu_wod_morskich_-_RM.pdf based on https://datras.ices.dk/Documents/Manuals/Addendum_1_WGBIFS_BITS_Manual_2011.pdf	"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	"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	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"	"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 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	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 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"	"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	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	The SAMBAH surveys; Acoustic monitoring. http://www.sambah.org/Methods.htm			Undersökningstyp: Syrehalt i bottenvatten, https://www.havochvatten.se/download/18.64f5b3211343cffddb2800020/1348912814827/Syrehalt+i+bottenvatten.pdf	Undersökningstyp: Syrehalt i bottenvatten, https://www.havochvatten.se/download/18.64f5b3211343cffddb2800020/1348912814827/Syrehalt+i+bottenvatten.pdf	The satellite calibrate their data against a fixed buoy each day as it passes over the buoy. The satellites reading is then compared with the buoy's registration. The raw data that are are transmitted from the satellite are brought together and each pixel in the images gets a mark of quality and areas where the images have missed some areas are marked.	The satellite calibrate their data against a fixed buoy each day as it passes over the buoy. The satellites reading is then compared with the buoy's registration. The raw data that are are transmitted from the satellite are brought together and each pixel in the images gets a mark of quality and areas where the images have missed some areas are marked.	HELCOM COMBINE Manual (Helcom 2014b, se Annex HC-C-4 för metod), will be replaced with HELCOM monitoring manual.	HELCOM COMBINE Manual (Helcom 2014b, se Annex HC-C-4 för metod), will be replaced with HELCOM monitoring manual.	"Växtplankton - HELCOM COMBINE Manual (Helcom 2014b, se Annex C6) Primärproduktion - HELCOM COMBINE Manual (Helcom 2014b)"	"Växtplankton - HELCOM COMBINE Manual (Helcom 2014b, se Annex C6) Primärproduktion - HELCOM COMBINE Manual (Helcom 2014b)"
Q9d - Description of alteration to method								\|\| 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_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_039 \|\|	The method can be seen in the manual.			1. Sample 10 stomachs per 1 cm size group of each predator species (cod and whiting). 2. A wide geographical coverage of samples should be obtained whenever possible and no more than 2 stomachs may be taken per cm group per haul and day (Exception: in SDs with few stations and/or low catches, a higher sampling frequency may be needed). 3. The 10 stomachs should be comprised of the categories (3) feeding, (4) empty or (5) containing only skeletal remains. Take care not to include stomachs that are everted or showing evidence of regurgitation (categories 1 & 2). 4. Preserve stomachs by freezing. Contents can be emptied into plastic bags before freezing. 5. Each sample should contain a unique label making it possible to obtain all the information	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.											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.																	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).																		Near real time data are collected and quality controlled	Near real time data are collected and quality controlled																															Time series started before 2002 are carried out according to the Swedish monitoring method described in "Provfiske med kustöversikttsnät, nätlänkar och ryssjor ".	Time series started before 2002 are carried out according to the Swedish monitoring method described in "Provfiske med kustöversikttsnät, nätlänkar och ryssjor ".
Q9e - Quality assurance								\|\| MP_037 \|\| Nationale SOP / Ringversuche; HELCOM / ICES RingversucheQualitätssicherungsprogramm des Bund-Länder-Messprogramms (BLMP); \|\| MP_041 \|\| national: Qualitätssicherungsprogramm des Bund-Länder-Messprogramms (BLMP); anderer: DIN EN ISO/IEC 17025 COMBINE ICESDataTypeGuide National Other	\|\| MP_037 \|\| Nationale SOP / Ringversuche; HELCOM / ICES RingversucheQualitätssicherungsprogramm des Bund-Länder-Messprogramms (BLMP); \|\| MP_041 \|\| national: Qualitätssicherungsprogramm des Bund-Länder-Messprogramms (BLMP); anderer: DIN EN ISO/IEC 17025 COMBINE ICESDataTypeGuide National Other	\|\| MP_039 \|\| national: Qualitätssicherungsprogramm des Bund-Länder-Messprogramms (BLMP); anderer: DIN EN ISO/IEC 17025 COMBINE National Other	\|\| MP_039 \|\| national: Qualitätssicherungsprogramm des Bund-Länder-Messprogramms (BLMP); anderer: DIN EN ISO/IEC 17025 COMBINE National Other	National	ICESDataTypeGuide	ICESDataTypeGuide	ICESDataTypeGuide	ICESDataTypeGuide	ICESDataTypeGuide	BEQUALM see link included above	Other see link included above	Other see link included above	Other see link included above	Other see link included above	Other see link included above	Other see link included above	see link included above	COMBINE QUASIMEM see link included above	ICESDataTypeGuide	ICESDataTypeGuide	ICESDataTypeGuide	National	ICESDataTypeGuide	National	COMBINE QUASIMEM see link included above	COMBINE QUASIMEM see link included above	COMBINE QUASIMEM see link included above	Bekendtgørelse om kvalitetskrav til miljømålinger (Statutory Order on Quality requirements in environmental analyses) https://www.retsinformation.dk/Forms/R0710.aspx?id=160496 Other	Other		COMBINE National standard defined by Finnish experts	National standard defined by Finnsih experts	Unknown	COMBINE	COMBINE	Unknown	Unknown	COMBINE	COMBINE	National Unknown	COMBINE	COMBINE	COMBINE	Contamination: National. Dredging: HELCOM. Construction: EIA legislation Other	COMBINE	COMBINE	National	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE			COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE	COMBINE								Based on https://docs.google.com/viewer?url=http://www.helcom.fi/Core%2520Indicators/HELCOM-CoreIndicator-Abundance_of_waterbirds_in_the_breeding_season.pdf&embedded=false&chrome=false&dov=1 Other	Based on http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-White-tail_eagle_productivity.pdf Other	ICESDataTypeGuide	COMBINE	ICESDataTypeGuide	Unknown	Unknown	Unknown	Unknown	Kvalitetssystem nationell miljöövervakning http://www.naturvardsverket.se/Stod-i-miljoarbetet/Vagledning-amnesvis/Miljoovervakning/Handledning/Kvalitetssystem/ National	Kvalitetssystem nationell miljöövervakning http://www.naturvardsverket.se/Stod-i-miljoarbetet/Vagledning-amnesvis/Miljoovervakning/Handledning/Kvalitetssystem/ National	Data quality assured internally when storing in the national database (KUL) through embedded and subjective plausibility checks. National	Data quality assured internally when storing in the national database (KUL) through embedded and subjective plausibility checks. National	Data quality assured internally when storing in the national database (KUL) through embedded and subjective plausibility checks. National	Data quality assured internally when storing in the national database (KUL) through embedded and subjective plausibility checks. National	The data host SLU are developing a system för QA/QC during 2014 Other	The data host SLU are developing a system för QA/QC during 2014 Other	National nationell miljöövervakning http://www.naturvardsverket.se/Stod-i-miljoarbetet/Vagledning-amnesvis/Miljoovervakning/Handledning/Kvalitetssystem/	National nationell miljöövervakning http://www.naturvardsverket.se/Stod-i-miljoarbetet/Vagledning-amnesvis/Miljoovervakning/Handledning/Kvalitetssystem/	Kvalitetssystem nationell miljöövervakning http://www.naturvardsverket.se/Stod-i-miljoarbetet/Vagledning-amnesvis/Miljoovervakning/Handledning/Kvalitetssystem/ National	Kvalitetssystem nationell miljöövervakning http://www.naturvardsverket.se/Stod-i-miljoarbetet/Vagledning-amnesvis/Miljoovervakning/Handledning/Kvalitetssystem/ National	Other Power andsensitivity analyses coordinated through HELCOM seal group. Methodology coordinated between Sweden, Denmark and Norway.	Other Power andsensitivity analyses coordinated through HELCOM seal group. Methodology coordinated between Sweden, Denmark and Norway.	Unknown	Unknown			COMBINE ICESDataTypeGuide IODE	COMBINE ICESDataTypeGuide IODE	BEQUALM	BEQUALM	COMBINE QUASIMEM	COMBINE QUASIMEM	(Intercalibrations BEQUALM Other QUASIMEM	(Intercalibrations BEQUALM Other QUASIMEM
Q9f - Quality control								RealValidation	RealValidation	RealValidation	RealValidation	DelayedValidation	RealandDelayedValidation	RealandDelayedValidation	RealandDelayedValidation	RealandDelayedValidation	RealandDelayedValidation	DelayedValidation	OtherQC	OtherQC	OtherQC	OtherQC	OtherQC	OtherQC			RealandDelayedValidation	RealandDelayedValidation	RealandDelayedValidation	DelayedValidation	RealandDelayedValidation	Unknown				OtherQC	OtherQC		RealandDelayedValidation	RealandDelayedValidation	Unknown	RealandDelayedValidation	RealandDelayedValidation	Unknown	Unknown	RealValidation	RealandDelayedValidation	Unknown	RealandDelayedValidation	RealandDelayedValidation	RealandDelayedValidation	Unknown	RealandDelayedValidation	RealandDelayedValidation	Unknown	RealandDelayedValidation	RealandDelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation			DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation								Unknown	Unknown	Unknown	RealandDelayedValidation	Unknown	Unknown	Unknown	OtherQC	OtherQC	Unknown	Unknown	DelayedValidation	DelayedValidation	DelayedValidation	DelayedValidation	OtherQC	OtherQC	Unknown	Unknown	Unknown	Unknown	RealValidation	RealValidation	DelayedValidation	DelayedValidation			DelayedValidation	DelayedValidation	OtherQC	OtherQC	OtherQC	OtherQC	OtherQC	OtherQC
Q9g - Spatial resolution of sampling	Q9g - Proportion of area covered %							100	100	100	100	0.3		2			2	50	100	50	100	50	100	10			2	2	2	0.3	2						100		100		100			15			100					100	100																																	100				50	50	20	20	100	100					39	39	10	10			100	100	100	100			100	100	100	100	20	20	20	20
Q9g - Spatial resolution of sampling	Q9g - No. of samples							\|\| 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_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_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.			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.	From each station we sample all species with length and weight and only selected species (see appendix 1b) for age and maturity.		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		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.			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.		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	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: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass	HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass	80 coastal sampling sites are sampled 4 times per year	HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity	HELCOM Monitoring manual - Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29 HELCOM Monitoring manual - Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice																													85 nests visited 3 times a year.		Phytoplankton - 90/year Zooplankton - 93/year		120 counting units annually.	120 counting units annually.	Approximately 410 counting units annually. In addition, country wide survey are carried out at irregular intervals, the last in 2004	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	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 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.	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	1 sample from 12 locations = 12 samples/year	25 samples from 3 locations = 75 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.	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	1 count per year a week during the moult	100 acoustic locations during 2, 5 years (2011-2013). No information regarding the next survey.	100 acoustic locations during 2, 5 years (2011-2013). No information regarding the next survey.			5091 samples from 547 locations during 2011	5091 samples from 547 locations during 2011	"Remote sensing - 1 image per day during three months = 92 images Harmful algaes - 2-24 samples from 19 locations = 230 samples/year"	"Remote sensing - 1 image per day during three months = 92 images Harmful algaes - 2-24 samples from 19 locations = 230 samples/year"	1-26 samples from 132 locations = 531 samples/year	1-26 samples from 132 locations = 531 samples/year	1-26 samples from 41 locations = 313 samples/year	1-26 samples from 41 locations = 313 samples/year
Q9i - Description of sample representivity												103 fishermen are participating with 3 sites eac. Indicating that each site represent 0.3% of the total. In total 52,000 individuals were caught in the last three year. Eelpout topped the list of species most frequently caught, mostly in fyke-nets. Next on the list was flounder with 23,000 individuals being caught over 3 years. An equal number of cod and eel were caught; 9,000 individuals. The catches reflect the fact that these species are among the most common and widespread species in Danish coastal waters.																		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																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												Monitoring is carried out in 16 monitoring sites 2 times a year	Monitoring is carried out in 16 monitoring sites 2 times a year	In coastal water bodies sampling is carried out 7 times a year, every year; in other coastal stations, territorial waters 3-4 times a year; in the off-shore areas 1-2 times a year (research vessel based monitoring)	In coastal water bodies sampling is carried out 7 times a year, every year; in other coastal stations, territorial waters 3-4 times a year; in the off-shore areas 1-2 times a year (research vessel based monitoring)	Research vessel based data are collected; operational data continuously	Research vessel based data are collected; operational data continuously	Research vessel based data are collected;	Research vessel based data are collected;	Research vessel based data are collected	Research vessel based data are collected	Research vessel based data are collected;	Research vessel based data are collected;	Research vessel based data are collected; operational data continuously	Research vessel based data are collected; operational data continuously											In Puck Bay the monitoring is performed 12 times a year.		See sub-programme Häckande sjöfågel, chapter Rumslig och tidsmässig täckning	See sub-programme Häckande sjöfågel, chapter Rumslig och tidsmässig täckning	See sub-programme Övervintrande 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 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 - 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 Migrerande fisk - Lax, parameter table and chapter Rumslig och tidsmässig täckning	See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning	See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning	See sub-programme Hälsotillstånd hos kustfisk, chapter Rumslig och tidsmässig täckning	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	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 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.	See sub-programme Bestånd av tumlare, chapter Rumslig och tidsmässig täckning See sub-programme Bestånd av tumlare, parameter table.			See sub-programme Pelagialens egenskaper - Syrekoncentration, chapter Rumslig och tidsmässig täckning	See sub-programme Pelagialens egenskaper - Syrekoncentration, chapter Rumslig och tidsmässig täckning	See sub-programme Skadliga algblomningar, chapter Rumslig och tidsmässig täckning	See sub-programme Skadliga algblomningar, chapter Rumslig och tidsmässig täckning	See sub-programme Växyplankton - Pigment, chapter Rumslig och tidsmässig täckning	See sub-programme Växyplankton - Pigment, chapter Rumslig och tidsmässig täckning	See sub-programme Växyplankton och pelagiska bakterier, chapter Rumslig och tidsmässig täckning See sub-programme Växyplankton och pelagiska bakterier, parameter table.	See sub-programme Växyplankton och pelagiska bakterier, chapter Rumslig och tidsmässig täckning See sub-programme Växyplankton och pelagiska bakterier, parameter table.
Q10a - Scale for aggregation of data								\|\| MP_037 \|\| Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. \|\| MP_041 \|\| \|\| Additional Data \|\| Other Other	\|\| MP_037 \|\| Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. \|\| MP_041 \|\| \|\| Additional Data \|\| Other Other	\|\| MP_039 \|\| Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. \|\| Additional Data \|\| Other Other	\|\| MP_039 \|\| Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. \|\| Additional Data \|\| Other Other	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region		Other Region national marine areas;	Region	National Other	Region	Region	Bothnian Bay Other	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	EU Region	Region	Region	Region	Region	Region			Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region	Region								Region	Region	Region	Region	Region	Other	Other	Other See 10b	Other See 10b	Other See 10b	Other See 10b	Region	Region	Region	Region	Region	Region	Other See 10b	Other See 10b	Other See 10b	Other See 10b	Region	Region	Region	Region			Region	Region	Subregion	Subregion	Region	Region	Region	Region
Q10b - Other scale for aggregation of data								\|\| MP_037 \|\| Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. \|\| MP_041 \|\| \|\| Additional Data \|\| Other	\|\| 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_039 \|\| Die Daten werden primär auf Stationsbasis belassen und können seegebietsweise zusammengefasst werden. \|\| Additional Data \|\| Other								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.															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	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.	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 Reproduktion hos havsörn, chapter Metoder							See sub-programme Hälsotillstånd hos kustfisk, chapter Metoder	See sub-programme Hälsotillstånd hos kustfisk, chapter Metoder	See sub-programme Hälsotillstånd hos säl, chapter Metoder	See sub-programme Hälsotillstånd hos säl, chapter Metoder
Q10c - Access to monitoring data	Q10c - Data type							DataProducts	DataProducts	DataProducts	DataProducts	ProcessedData	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	ProcessedData	ProcessedData	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData	ProcessedData DataProducts	UnprocessedData	UnprocessedData	UnprocessedData	ProcessedData	UnprocessedData ProcessedData	ProcessedData Simulated		ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData			ProcessedData	ProcessedData	ProcessedData	ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	ProcessedData	ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	ProcessedData	ProcessedData	ProcessedData	ProcessedData								UnprocessedData	UnprocessedData	UnprocessedData	UnprocessedData	UnprocessedData	UnprocessedData	UnprocessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData ProcessedData DataProducts	UnprocessedData DataProducts	UnprocessedData DataProducts	UnprocessedData DataProducts Simulated	UnprocessedData DataProducts Simulated			UnprocessedData DataProducts	UnprocessedData DataProducts	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData	UnprocessedData ProcessedData
Q10c - Access to monitoring data	Q10c - Data access mechanism							LocationInternationalDC	LocationInternationalDC	LocationInternationalDC	LocationInternationalDC	LocationNationalDC	LocationInternationalDC	LocationInternationalDC	LocationInternationalDC	LocationInternationalDC	LocationInternationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationInternationalDC	LocationInternationalDC	LocationInternationalDC	LocationNationalDC	LocationInternationalDC	LocationInternationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC		LocationNationalDC	URLview	URLview	URLview	URLview	URLview	URLview	URLview	URLview	URLview	URLview	URLview	URLview	URLview	URLview	URLview	URLview	LocationInternationalDC	URLview	URLdownload	URLdownload	URLdownload	URLdownload			LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationInternationalDC	LocationInternationalDC	LocationNationalDC	LocationNationalDC								URLdownload	URLdownload	URLdownload	URLdownload	URLdownload	LocationNationalDC	LocationNationalDC	LocationInternationalDC	LocationInternationalDC	URLdownload	URLdownload	LocationNationalDC	LocationNationalDC	LocationNationalDC	LocationNationalDC	URLdownload	URLdownload	URLdownload	URLdownload	URLdownload	URLdownload	URLdownload	URLdownload	LocationNationalDC	LocationNationalDC			URLdownload	URLdownload	URLdownload	URLdownload	URLdownload	URLdownload	URLdownload	URLdownload
Q10c - Access to monitoring data	Q10c - Data access rights							Open	Open	Open	Open	RestrictedSpecific	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	RestrictedSpecific	Open	Open	Open	Open	Open	Open	Open		RestrictedGeneral	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open			Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open								Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open	Open			Open	Open	Open	Open	Open	Open	Open	Open
Q10c - Access to monitoring data	Q10c - INSPIRE standard							\|\| MP_037, MP_041 \|\| \|\| Additional Data \|\| EnvMonitoringFacilities	\|\| MP_037, MP_041 \|\| \|\| Additional Data \|\| EnvMonitoringFacilities	\|\| MP_039 \|\| \|\| Additional Data \|\| EnvMonitoringFacilities	\|\| MP_039 \|\| \|\| Additional Data \|\| EnvMonitoringFacilities	OceanographicFeatures SeaRegions SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	SeaRegions SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	HabitatsBiotopes SpeciesDistribution	HabitatsBiotopes SpeciesDistribution	HabitatsBiotopes SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	OceanographicFeatures SeaRegions SpeciesDistribution	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		SeaRegions SpeciesDistribution	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	HabitatsBiotopes SeaRegions SpeciesDistribution	HabitatsBiotopes SeaRegions SpeciesDistribution	ManagementZonesReportingUnits	Hydrography	Hydrography	ManagementZonesReportingUnits	ManagementZonesReportingUnits	ManagementZonesReportingUnits	ManagementZonesReportingUnits			SpeciesDistribution	SpeciesDistribution	SpeciesDistribution	SpeciesDistribution	OceanographicFeatures	OceanographicFeatures	OceanographicFeatures	OceanographicFeatures	OceanographicFeatures	OceanographicFeatures	OceanographicFeatures	OceanographicFeatures	OceanographicFeatures	OceanographicFeatures								EnvMonitoringFacilities	EnvMonitoringFacilities	EnvMonitoringFacilities	EnvMonitoringFacilities	EnvMonitoringFacilities
Q10c - Access to monitoring data	Q10c Date data are available							2015-01	2015-01	2015-01	2015-01	2014-09	2015-04	2015-04	2015-04	2015-04	2015-04	2014-12	2014-11	2014-11	2014-11	2014-11	2014-11	2014-11	2015-04	2015-04	2015-04	2015-04	2015-04	2015-10	2015-04	2014-12	2014-12	2014-12	2015-04	2014-12	1990-01		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	2015-12	2015-12		2015-12	2014-12	2014-12	2014-12	2014-12			1990-12	1990-12	1980-12	1980-12	2011-06	2011-06	1980-12	1980-12	2011-06	2011-06	1972-12	1972-12	2011-06	2011-06								2015-12	2015-12	2015-12	2015-12	2015-12	2016-01	2016-01	2014-01	2014-01	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09			2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09	2014-09
Q10c - Access to monitoring data	Q10c - Data update frequency							Unknown	Unknown	Other	Other	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	2weekly	2weekly	Yearly	Yearly	Yearly		Yearly	Yearly	Asneeded	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	6yearly	Unknown	Yearly	Unknown	Yearly	Unknown	Yearly	Yearly	Yearly	Yearly			Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly								Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly			Yearly	Yearly	Other	Other			Yearly	Yearly	Other	Other	Yearly	Yearly
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&other=1&id=bfg) erfasst und zugänglich gemacht. Die Bezugsquelle für die Daten aus den nationalen Messprogrammen wird in den Metadaten festgelegt. Die HELCOM- und OSPAR-relevanten Daten aus den hydrografischen, biologischen und chemischen Messprogrammen werden regelmäßig dem ICES (international data centre) übermittelt. Die EEA kann diese Daten wie bisher über den ICES beziehen. Die Bezugswege für die darüber hinaus gehenden Daten und Produkte befinden sich im Aufbau. Die entsprechenden Metadaten werden die Bezugsquellen ausweisen.	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&other=1&id=bfg) erfasst und zugänglich gemacht. Die Bezugsquelle für die Daten aus den nationalen Messprogrammen wird in den Metadaten festgelegt. Die HELCOM- und OSPAR-relevanten Daten aus den hydrografischen, biologischen und chemischen Messprogrammen werden regelmäßig dem ICES (international data centre) übermittelt. Die EEA kann diese Daten wie bisher über den ICES beziehen. Die Bezugswege für die darüber hinaus gehenden Daten und Produkte befinden sich im Aufbau. Die entsprechenden Metadaten werden die Bezugsquellen ausweisen.	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&other=1&id=bfg) erfasst und zugänglich gemacht. Die Bezugsquelle für die Daten aus den nationalen Messprogrammen wird in den Metadaten festgelegt. Die HELCOM- und OSPAR-relevanten Daten aus den hydrografischen, biologischen und chemischen Messprogrammen werden regelmäßig dem ICES (international data centre) übermittelt. Die EEA kann diese Daten wie bisher über den ICES beziehen. Die Bezugswege für die darüber hinaus gehenden Daten und Produkte befinden sich im Aufbau. Die entsprechenden Metadaten werden die Bezugsquellen ausweisen.	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&other=1&id=bfg) erfasst und zugänglich gemacht. Die Bezugsquelle für die Daten aus den nationalen Messprogrammen wird in den Metadaten festgelegt. Die HELCOM- und OSPAR-relevanten Daten aus den hydrografischen, biologischen und chemischen Messprogrammen werden regelmäßig dem ICES (international data centre) übermittelt. Die EEA kann diese Daten wie bisher über den ICES beziehen. Die Bezugswege für die darüber hinaus gehenden Daten und Produkte befinden sich im Aufbau. Die entsprechenden Metadaten werden die Bezugsquellen ausweisen.	A national data base is holding the data. The project will continue for the periode 2014-2016. Reference: Kristensen, L.D., Støttrup, J.G., Andersen, S. K. & Degel, H. 2014. Registrering af fangster i de danske kystområder med standardredskaber. Nøglefiskerrapport 2011-2013. DTU Aqua-rapport nr. 286-2014. Institut for Akvatiske Ressourcer, Danmarks Tekniske Universitet, 100 p. + bilag.	In ICES DATRAS database.	In ICES Regional data base (RDB).	In ICES DATRAS database.	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.	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.	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.	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.		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	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: Zooplankton mean size and total abundance - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Zooplankton_mean_size_and_total_abundance.pdf Raw data available on NOAA/COPEPOD-plankton database - http://www.st.nmfs.noaa.gov/plankton/content/region_baltic.html More information on data access is available in the HELCOM Monitoring manual - Sub-programme: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass	ICES data portal - http://www.ices.dk/marine-data/data-portals/Pages/DOME.aspx HELCOM Data and Map services - http://helcom.fi/baltic-sea-trends/data-maps Soon also available on Finnish open data portal OIVA - https://wwwp2.ymparisto.fi/scripts/oiva.asp (in Finnish) More information on data access is available in the HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass	Information can be found at EEA State of bathing water site - http://www.eea.europa.eu/themes/water/interactive/bathing/state-of-bathing-waters-1 and at the National Supervisory Authority for Welfare and Health - http://www.valvira.fi/files/ohjeet/Yleisten_uimarantojen_uimaveden_valvonta.pdf (in Finnish)	The data is open access and available to the EEA though HELCOM and ICES Web access points. Finnish Meteorological Institute Open Data Manual - http://en.ilmatieteenlaitos.fi/open-data-manual SYKE public data portal OIVA in Finnish - https://wwwp2.ymparisto.fi/scripts/oiva.asp Information on data access is also available in the HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity	Finnish Meteorological Institute Open Data Manual - http://en.ilmatieteenlaitos.fi/open-data-manual More information on data access is available in the HELCOM Monitoring manual: - Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29 - Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice	Gathered monitoring data is stored in databases at Environmental Protection Agency and Nature Research Centre (http://www.gamtostyrimai.lt/en/).	Gathered monitoring data is stored in databases at Environmental Protection Agency and Nature Research Centre (http://www.gamtostyrimai.lt/en/).	Gathered monitoring data is stored in databases at Environmental Protection Agency and Nature Research Centre (http://www.gamtostyrimai.lt/en/).	Gathered monitoring data is stored in databases at Environmental Protection Agency and Nature Research Centre (http://www.gamtostyrimai.lt/en/).			Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency	Gathered data can be accessed at Environmental Protection Agency								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	Direct encoding and sending to EEA and ICES database.	EEA EIONET for WFD monitoring.	See sub-programme Övervintrande sjöfågel, chapter Var finns data, and Metoder	See sub-programme Övervintrande sjöfågel, chapter Var finns data, and Metoder	See sub-programme Övervintrande sjöfågel, chapter Var finns data	See sub-programme Övervintrande sjöfågel, chapter Var finns data	See sub-programme Reproduktion hos havsörn, chapter Var finns data	See sub-programme Reproduktion hos havsörn, chapter Var finns data	See sub-programme Migrerande fiskarter - ål, chapter Var finns data	See sub-programme Migrerande fiskarter - ål, chapter Var finns data	See sub-programme Migrerande fiskarter - lax, chapter Var finns data	See sub-programme Migrerande fiskarter - lax, chapter Var finns data	See sub-programme Kustprovfiske, chapter Var finns data	See sub-programme Kustprovfiske, chapter Var finns data	See sub-programme Hälsotillstånd hos kustfisk, chapter Var finns data	See sub-programme Hälsotillstånd hos kustfisk, chapter Var finns data	Se sub-programme Hälsotillstånd hos säl, chapter Var finns data	Se sub-programme Hälsotillstånd hos säl, chapter Var finns data	See sub-programme Bestånd av säl, chapter Var finns data	See sub-programme Bestånd av säl, chapter Var finns data	See sub-programme Bestånd av tumlare, chapter Var finns data	See sub-programme Bestånd av tumlare, chapter Var finns data			See sub-programme Pelagialens egenskaper - Syrekoncentration, chapter Var finns data	See sub-programme Pelagialens egenskaper - Syrekoncentration, chapter Var finns data	See sub-programme Skadliga algblomningar, chapter Var finns data?	See sub-programme Skadliga algblomningar, chapter Var finns data?	See sub-programme Växyplankton - Pigment, chapter Var finns data	See sub-programme Växyplankton - Pigment, chapter Var finns data	See sub-programme Växtplankton och pelagiska bakterier, chapter Var finns data	See sub-programme Växtplankton och pelagiska bakterier, chapter Var finns data