Art11

Member State report / Art11 / 2020 / D1-F / Sweden / Baltic Sea

Report type	Member State report to Commission
MSFD Article	Art. 11 Monitoring programmes (and Art. 17 updates)
Report due	2020-10-15
GES Descriptor	D1 Fish
Member State	Sweden
Region/subregion	Baltic Sea
Reported by	Swedish Agency for Marine and Water Management Gullbergs Strandgata 15, 411 04 Göteborg Box 11930,
Report date	2020-10-16
Report access	ART11_SE_MONprog_v5.xml ART11_SE_MONstrat_v4.xml

Simplified table

Descriptor	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4	D1.4
Monitoring strategy description	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.	The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
Coverage of GES criteria	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024
Gaps and plans	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.	Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Related targets	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek	ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek BALSE-C.3_Population_fisk_ålder_storlek_bestånd BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
Coverage of targets	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014
Related measures	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'	ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' ANSSE-M034 - 'National environmental targets' ANSSE-M039 - 'Common Fisheries Policy' BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters' BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters' BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks' BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures' BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species' BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities' BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally' BALSE-M039 - 'Common Fisheries Policy'
Coverage of measures	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014
Related monitoring programmes	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth	SE-D1D2D7-outfalls SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D8-fishhealth
Programme code	SE-D1D2D7-outfalls	SE-D1D2D7-outfalls	SE-D1D2D7-outfalls	SE-D1D2D7-outfalls	SE-D1D2D7-outfalls	SE-D1D2D7-outfalls	SE-D1D2D7-outfalls	SE-D1D2D7-outfalls	SE-D1D2D7-outfalls	SE-D1D3-bycatch	SE-D1D3-bycatch	SE-D1D3-comfishing	SE-D1D3-comfishing	SE-D1D3-eel	SE-D1D3-eel	SE-D1D3-recreationalfishing	SE-D1D3-recreationalfishing	SE-D1D3-salmon	SE-D1D3-salmon	SE-D1D3D4-coastalfish	SE-D1D3D4-coastalfish	SE-D1D3D4-coastalfish	SE-D1D3D4-coastalfish	SE-D1D3D4-coastalfish	SE-D1D3D4-coastalfish	SE-D1D3D4-coastalfish	SE-D1D3D4-coastalfish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D3D4-offshorefish	SE-D1D8-fishhealth	SE-D1D8-fishhealth	SE-D1D8-fishhealth	SE-D1D8-fishhealth
Programme name	Effects of outfalls from power stations	Effects of outfalls from power stations	Effects of outfalls from power stations	Effects of outfalls from power stations	Effects of outfalls from power stations	Effects of outfalls from power stations	Effects of outfalls from power stations	Effects of outfalls from power stations	Effects of outfalls from power stations	Bycatch	Bycatch	Commercial fisheries	Commercial fisheries	Migratory fish (eel)	Migratory fish (eel)	Recreational fisheries	Recreational fisheries	Migratory fish (salmon)	Migratory fish (salmon)	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Offshore fish	Offshore fish	Offshore fish	Offshore fish	Offshore fish	Offshore fish	Offshore fish	Offshore fish	Offshore fish	Offshore fish	Offshore fish	Offshore fish	Fish health status	Fish health status	Fish health status	Fish health status
Update type	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	New programme	New programme	Modified from 2014	Modified from 2014	New programme	New programme	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014
Old programme codes	ANSSE-HYDRO-D72-Kylvatten BALSE-HYDRO-D72-Kylvatten	ANSSE-HYDRO-D72-Kylvatten BALSE-HYDRO-D72-Kylvatten	ANSSE-HYDRO-D72-Kylvatten BALSE-HYDRO-D72-Kylvatten	ANSSE-HYDRO-D72-Kylvatten BALSE-HYDRO-D72-Kylvatten	ANSSE-HYDRO-D72-Kylvatten BALSE-HYDRO-D72-Kylvatten	ANSSE-HYDRO-D72-Kylvatten BALSE-HYDRO-D72-Kylvatten	ANSSE-HYDRO-D72-Kylvatten BALSE-HYDRO-D72-Kylvatten	ANSSE-HYDRO-D72-Kylvatten BALSE-HYDRO-D72-Kylvatten	ANSSE-HYDRO-D72-Kylvatten BALSE-HYDRO-D72-Kylvatten	ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Utkast			ANSSE-COMFISH-D314-Al BALSE-COMFISH-D314-Al	ANSSE-COMFISH-D314-Al BALSE-COMFISH-D314-Al			BALSE-COMFISH-D314-Lax	BALSE-COMFISH-D314-Lax	ANSSE-Fish-D14-Kust ANSSE-Fish-D14-Tral BALSE-Fish-D14-Kust	ANSSE-Fish-D14-Kust ANSSE-Fish-D14-Tral BALSE-Fish-D14-Kust	ANSSE-Fish-D14-Kust ANSSE-Fish-D14-Tral BALSE-Fish-D14-Kust	ANSSE-Fish-D14-Kust ANSSE-Fish-D14-Tral BALSE-Fish-D14-Kust	ANSSE-Fish-D14-Kust ANSSE-Fish-D14-Tral BALSE-Fish-D14-Kust	ANSSE-Fish-D14-Kust ANSSE-Fish-D14-Tral BALSE-Fish-D14-Kust	ANSSE-Fish-D14-Kust ANSSE-Fish-D14-Tral BALSE-Fish-D14-Kust	ANSSE-Fish-D14-Kust ANSSE-Fish-D14-Tral BALSE-Fish-D14-Kust	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-COMFISH-D3-Bottenlevande ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Bottenlevande BALSE-COMFISH-D3-Pelagisk BALSE-COMFISH-D3-Utkast	ANSSE-HAZ-D814-Fiskhalsa BALSE-HAZ-D814-Fiskhalsa	ANSSE-HAZ-D814-Fiskhalsa BALSE-HAZ-D814-Fiskhalsa	ANSSE-HAZ-D814-Fiskhalsa BALSE-HAZ-D814-Fiskhalsa	ANSSE-HAZ-D814-Fiskhalsa BALSE-HAZ-D814-Fiskhalsa
Programme description	A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.	A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.	A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.	A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.	A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.	A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.	A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.	A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.	A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.	In the regular sampling carried out on board commercial fishing vessels in accordance with EU data collection regulations ((EU) 2017/1004, (EU) 2016/1251), as well as the regulation on the conservation of fishery resources and the protection of marine ecosystems (EU ) 2019/1241, information regarding by-catch is obtained. All fish species, commercial shellfish, mammals and birds are noted. Sampling takes place mainly on vessels fishing with various bottom trawls. Data collection carried out according to the EU data collection regulations is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES´s various expert groups (for by-catches mainly WGBYC). Sweden participates actively in these groups. Pilot studies were carried out in 2017-2019 with the aim of conducting by-catch sampling in 2020 in fisheries that use passive gear (nets and hooks). The purpose is to increase knowledge about by-catches in these fisheries, to test whether it is possible to estimate by-catches by having observers on board fishing boats, and if this is an effective method. Sampling of nets in the Sound and in the Kattegat will be included in the regular sampling from 2020. However, no ongoing monitoring of passive gear is currently planned in the Baltic Proper as previous pilots observed fewer by-catches there. So based on risk, monitoring in the Sound and Kattegatt are therefore prioritized. The Skagerrak could possibly be added after the pilot study there is completed in 2021. The pilot studies have shown that it also works to monitor the fish with passive gear with the help of observers (the challenge is that the vessels are small). However, the question remains whether this is the most effective way of estimating the total amount of by-catches in the fisheries. The problem is that observers can only cover a small part of the total fishing effort and that by-catches of many species (such as harbour porpoises and various birds) are relatively uncommon. This means that there will be few observations and thus uncertainty in the estimates of the total amount of by-catches. In 2020, therefore, a new pilot project was initiated where surveillance with the help of cameras is tested and compared with surveillance with the help	In the regular sampling carried out on board commercial fishing vessels in accordance with EU data collection regulations ((EU) 2017/1004, (EU) 2016/1251), as well as the regulation on the conservation of fishery resources and the protection of marine ecosystems (EU ) 2019/1241, information regarding by-catch is obtained. All fish species, commercial shellfish, mammals and birds are noted. Sampling takes place mainly on vessels fishing with various bottom trawls. Data collection carried out according to the EU data collection regulations is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES´s various expert groups (for by-catches mainly WGBYC). Sweden participates actively in these groups. Pilot studies were carried out in 2017-2019 with the aim of conducting by-catch sampling in 2020 in fisheries that use passive gear (nets and hooks). The purpose is to increase knowledge about by-catches in these fisheries, to test whether it is possible to estimate by-catches by having observers on board fishing boats, and if this is an effective method. Sampling of nets in the Sound and in the Kattegat will be included in the regular sampling from 2020. However, no ongoing monitoring of passive gear is currently planned in the Baltic Proper as previous pilots observed fewer by-catches there. So based on risk, monitoring in the Sound and Kattegatt are therefore prioritized. The Skagerrak could possibly be added after the pilot study there is completed in 2021. The pilot studies have shown that it also works to monitor the fish with passive gear with the help of observers (the challenge is that the vessels are small). However, the question remains whether this is the most effective way of estimating the total amount of by-catches in the fisheries. The problem is that observers can only cover a small part of the total fishing effort and that by-catches of many species (such as harbour porpoises and various birds) are relatively uncommon. This means that there will be few observations and thus uncertainty in the estimates of the total amount of by-catches. In 2020, therefore, a new pilot project was initiated where surveillance with the help of cameras is tested and compared with surveillance with the help	Commercial fishing in this case refers to the commercial fishing that requires a fishing license and has an obligation to report its fishing activity. The obligation to report their catches and fishing activities is governed by both EU legislation and Swedish legislation. This information is used for the national quota allocation for fish stocks and as a basis for the biological stock estimate (see also programmes Offshore fish and coastal fish). Economic statistics are collected to monitor economic drivers in the fisheries sector. The statistics are collected to meet the requirements from the EU via Regulation (EU) 2017/1004 and implementing decisions (EU) 2019/909 and (EU) 2019/910. In addition to this reporting, statistics are used within the Swedish Fisheries Administration. In addition to the pressure in the form of extracting fish, the monitoring of other parts of the fishing activities' impact is described in the programmes Physical disturbance and loss (bottom trawling) and in By-catch.	Commercial fishing in this case refers to the commercial fishing that requires a fishing license and has an obligation to report its fishing activity. The obligation to report their catches and fishing activities is governed by both EU legislation and Swedish legislation. This information is used for the national quota allocation for fish stocks and as a basis for the biological stock estimate (see also programmes Offshore fish and coastal fish). Economic statistics are collected to monitor economic drivers in the fisheries sector. The statistics are collected to meet the requirements from the EU via Regulation (EU) 2017/1004 and implementing decisions (EU) 2019/909 and (EU) 2019/910. In addition to this reporting, statistics are used within the Swedish Fisheries Administration. In addition to the pressure in the form of extracting fish, the monitoring of other parts of the fishing activities' impact is described in the programmes Physical disturbance and loss (bottom trawling) and in By-catch.	Eels are monitored along the West Coast and the Baltic Sea. Eels along the Swedish coast are found in three life stages, which are glass eels, yellow eels and silver eels. The monitoring aims to provide a knowledge base for the management of eels. On the West Coast, eels are monitored through fisheries-independent sampling because eel fishing on the West Coast, north of Torekov, is not permitted. In the Baltic Sea, eels are monitored by sampling in commercial fishing. Most studies regarding migratory young eels are done in traps that catch very small yellow eels on migration in running water, in two studies migratory silver eels are caught. The programme describes the composition with respect to age and size at all stages of life. In addition, marking/tagging is done with the aim of estimating the proportion that is caught in commercial fishing, at the same time as an estimate is made of the size of the coastal stock. This monitoring programme applies to eels in the sea. Eels are also caught in freshwater to monitor the impact of, among other things, fishing and hydropower. This monitoring is not described here. Sweden's monitoring is coordinated with other countries that carry out monitoring of eels, by Sweden reporting every three years to ICES, who compiles an overview based on the countries' reporting to an overview analysis that covers the entire eel range (Europe, North Africa and West Asia). Monitoring data from Sweden and other countries are used here, to examine weighted trends in the occurrence of eels, the nature of eels, threats to eels and recommendations for a better knowledge base. Ices also issues annual scientific advice on the eel. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate.	Eels are monitored along the West Coast and the Baltic Sea. Eels along the Swedish coast are found in three life stages, which are glass eels, yellow eels and silver eels. The monitoring aims to provide a knowledge base for the management of eels. On the West Coast, eels are monitored through fisheries-independent sampling because eel fishing on the West Coast, north of Torekov, is not permitted. In the Baltic Sea, eels are monitored by sampling in commercial fishing. Most studies regarding migratory young eels are done in traps that catch very small yellow eels on migration in running water, in two studies migratory silver eels are caught. The programme describes the composition with respect to age and size at all stages of life. In addition, marking/tagging is done with the aim of estimating the proportion that is caught in commercial fishing, at the same time as an estimate is made of the size of the coastal stock. This monitoring programme applies to eels in the sea. Eels are also caught in freshwater to monitor the impact of, among other things, fishing and hydropower. This monitoring is not described here. Sweden's monitoring is coordinated with other countries that carry out monitoring of eels, by Sweden reporting every three years to ICES, who compiles an overview based on the countries' reporting to an overview analysis that covers the entire eel range (Europe, North Africa and West Asia). Monitoring data from Sweden and other countries are used here, to examine weighted trends in the occurrence of eels, the nature of eels, threats to eels and recommendations for a better knowledge base. Ices also issues annual scientific advice on the eel. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate.	Recreational fishing in Sweden is defined as all fishing that does not take place with the support of a commercial fishing license. Recreational fishing includes both fishing with hand gear (eg rod) and catching gear (eg nets). Recreational fishing in Sweden is extensive and therefore good knowledge is needed about the practitioners, where to fish and what is caught. As part of the work to understand and describe the scope and impact, statistics on recreational fishing have been collected since the 1970s to form the basis for decisions within the administration. The first survey was part of the 1973 fishing water investigation, which was also followed up during the 1990s. In 2011, the SwAM became the coordinating agency for official statistics in the area of fishing and was thus given the responsibility to annually collect statistics regarding the extent of recreational fishing in Sweden. This collection takes place via a national survey that started in 2013 and is progressing in roughly the same direction and design today. In addition to the national survey, several fishing sites are visited on a regular basis since 2012. Data collection is carried out annually in the Sound and the southern Baltic Sea in accordance with EU regulations ((EU) 2019/909 and (EU) 2019/910). The data collection aims to cover the fishing for cod and by-catches in this fishery (see programme Bycatch). Monitoring frequency is three times per year (4-monthly). A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. An ongoing project initiated by Sportfiskarna is about developing an application – FångstDatabanken (Citizen science) for catch reporting. SwAM has since the start in 2012 been part of their reference and development group. Data collection carried out under the EU Data Collection Regulation is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups, RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES 'various expert groups (for recreational fishing, especially WGRFS). Sweden participates actively in these g	Recreational fishing in Sweden is defined as all fishing that does not take place with the support of a commercial fishing license. Recreational fishing includes both fishing with hand gear (eg rod) and catching gear (eg nets). Recreational fishing in Sweden is extensive and therefore good knowledge is needed about the practitioners, where to fish and what is caught. As part of the work to understand and describe the scope and impact, statistics on recreational fishing have been collected since the 1970s to form the basis for decisions within the administration. The first survey was part of the 1973 fishing water investigation, which was also followed up during the 1990s. In 2011, the SwAM became the coordinating agency for official statistics in the area of fishing and was thus given the responsibility to annually collect statistics regarding the extent of recreational fishing in Sweden. This collection takes place via a national survey that started in 2013 and is progressing in roughly the same direction and design today. In addition to the national survey, several fishing sites are visited on a regular basis since 2012. Data collection is carried out annually in the Sound and the southern Baltic Sea in accordance with EU regulations ((EU) 2019/909 and (EU) 2019/910). The data collection aims to cover the fishing for cod and by-catches in this fishery (see programme Bycatch). Monitoring frequency is three times per year (4-monthly). A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. An ongoing project initiated by Sportfiskarna is about developing an application – FångstDatabanken (Citizen science) for catch reporting. SwAM has since the start in 2012 been part of their reference and development group. Data collection carried out under the EU Data Collection Regulation is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups, RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES 'various expert groups (for recreational fishing, especially WGRFS). Sweden participates actively in these g	The monitoring includes the collection of biological data for wild salmon stocks (salmon rivers) as well as statistics for releases and fishing for both wild and farmed salmon. The purpose of the monitoring is to monitor the status and development of wild salmon stocks and to investigate the effects of fishing and hydropower. The purpose of the biological advice is to contribute to the overall goals for salmon management being met both nationally and internationally. These goals are to protect and rebuild weak wild salmon stocks so that they can gradually reach the management goal of Maximum Sustainable Yield (MSY). Sweden's monitoring is coordinated with similar work in other countries, through guidelines and agreements developed within ICES, the North Atlantic Salmon Conservation Organization (NASCO), the Regional Coordination Groups (EU RCG) and HELCOM. Sweden actively participates in the regional coordination.	The monitoring includes the collection of biological data for wild salmon stocks (salmon rivers) as well as statistics for releases and fishing for both wild and farmed salmon. The purpose of the monitoring is to monitor the status and development of wild salmon stocks and to investigate the effects of fishing and hydropower. The purpose of the biological advice is to contribute to the overall goals for salmon management being met both nationally and internationally. These goals are to protect and rebuild weak wild salmon stocks so that they can gradually reach the management goal of Maximum Sustainable Yield (MSY). Sweden's monitoring is coordinated with similar work in other countries, through guidelines and agreements developed within ICES, the North Atlantic Salmon Conservation Organization (NASCO), the Regional Coordination Groups (EU RCG) and HELCOM. Sweden actively participates in the regional coordination.	Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish	Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish	Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish	Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish	Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish	Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish	Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish	Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	Monitoring, where biological effects are studied at both subcellular and cellular levels, can be used to describe the general state of health of different organisms and provides an opportunity to demonstrate the toxicity of unknown and known substances in a study area. The national monitoring of the health status of coastal fish aims to use proven and sensitive methods to demonstrate the presence and effects in fish of a possible large-scale impact of hazardous substances in coastal reference areas in the Baltic Sea and the North Sea. The aim of the monitoring is to be able to describe the current state of the environment in coastal reference areas regarding effects of mainly hazardous substances on the state of fish health by following time trends of biochemical, physiological, histological and pathological effect variables in fish. The surveys shall also provide reference data for surveys on fish in regionally and locally affected areas and provide a basis for monitoring environmental quality objectives, regional environmental objectives and the effects of measures taken to reduce chemical emissions. The national monitoring of fish health began with surveys of perch in 1988 in the Baltic Sea and in 1989 the programme was expanded with eelpout from the North Sea. During 2020-2021, the monitoring of the effects of hazardous substances will be evaluated in order to be able to optimize the monitoring programmes both in terms of coverage and costs and to provide a better basis for state assessment and determining the causes of the effects.	Monitoring, where biological effects are studied at both subcellular and cellular levels, can be used to describe the general state of health of different organisms and provides an opportunity to demonstrate the toxicity of unknown and known substances in a study area. The national monitoring of the health status of coastal fish aims to use proven and sensitive methods to demonstrate the presence and effects in fish of a possible large-scale impact of hazardous substances in coastal reference areas in the Baltic Sea and the North Sea. The aim of the monitoring is to be able to describe the current state of the environment in coastal reference areas regarding effects of mainly hazardous substances on the state of fish health by following time trends of biochemical, physiological, histological and pathological effect variables in fish. The surveys shall also provide reference data for surveys on fish in regionally and locally affected areas and provide a basis for monitoring environmental quality objectives, regional environmental objectives and the effects of measures taken to reduce chemical emissions. The national monitoring of fish health began with surveys of perch in 1988 in the Baltic Sea and in 1989 the programme was expanded with eelpout from the North Sea. During 2020-2021, the monitoring of the effects of hazardous substances will be evaluated in order to be able to optimize the monitoring programmes both in terms of coverage and costs and to provide a better basis for state assessment and determining the causes of the effects.	Monitoring, where biological effects are studied at both subcellular and cellular levels, can be used to describe the general state of health of different organisms and provides an opportunity to demonstrate the toxicity of unknown and known substances in a study area. The national monitoring of the health status of coastal fish aims to use proven and sensitive methods to demonstrate the presence and effects in fish of a possible large-scale impact of hazardous substances in coastal reference areas in the Baltic Sea and the North Sea. The aim of the monitoring is to be able to describe the current state of the environment in coastal reference areas regarding effects of mainly hazardous substances on the state of fish health by following time trends of biochemical, physiological, histological and pathological effect variables in fish. The surveys shall also provide reference data for surveys on fish in regionally and locally affected areas and provide a basis for monitoring environmental quality objectives, regional environmental objectives and the effects of measures taken to reduce chemical emissions. The national monitoring of fish health began with surveys of perch in 1988 in the Baltic Sea and in 1989 the programme was expanded with eelpout from the North Sea. During 2020-2021, the monitoring of the effects of hazardous substances will be evaluated in order to be able to optimize the monitoring programmes both in terms of coverage and costs and to provide a better basis for state assessment and determining the causes of the effects.	Monitoring, where biological effects are studied at both subcellular and cellular levels, can be used to describe the general state of health of different organisms and provides an opportunity to demonstrate the toxicity of unknown and known substances in a study area. The national monitoring of the health status of coastal fish aims to use proven and sensitive methods to demonstrate the presence and effects in fish of a possible large-scale impact of hazardous substances in coastal reference areas in the Baltic Sea and the North Sea. The aim of the monitoring is to be able to describe the current state of the environment in coastal reference areas regarding effects of mainly hazardous substances on the state of fish health by following time trends of biochemical, physiological, histological and pathological effect variables in fish. The surveys shall also provide reference data for surveys on fish in regionally and locally affected areas and provide a basis for monitoring environmental quality objectives, regional environmental objectives and the effects of measures taken to reduce chemical emissions. The national monitoring of fish health began with surveys of perch in 1988 in the Baltic Sea and in 1989 the programme was expanded with eelpout from the North Sea. During 2020-2021, the monitoring of the effects of hazardous substances will be evaluated in order to be able to optimize the monitoring programmes both in terms of coverage and costs and to provide a better basis for state assessment and determining the causes of the effects.
Monitoring purpose	Environmental state and impacts Human activities causing the pressures Pressures at source Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures at source Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures at source Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures at source Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures at source Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures at source Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures at source Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures at source Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source	Effectiveness of measures Human activities causing the pressures Pressures at source	Effectiveness of measures Human activities causing the pressures Pressures at source	Effectiveness of measures Human activities causing the pressures Pressures at source	Environmental state and impacts	Environmental state and impacts	Effectiveness of measures Human activities causing the pressures Pressures at source	Effectiveness of measures Human activities causing the pressures Pressures at source	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Effectiveness of measures Environmental state and impacts	Environmental state and impacts	Environmental state and impacts	Environmental state and impacts	Environmental state and impacts
Other policies and conventions	Monitoring programme targeting at national legislation	Monitoring programme targeting at national legislation	Monitoring programme targeting at national legislation	Monitoring programme targeting at national legislation	Monitoring programme targeting at national legislation	Monitoring programme targeting at national legislation	Monitoring programme targeting at national legislation	Monitoring programme targeting at national legislation	Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation Water Framework Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation Water Framework Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation Water Framework Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation Water Framework Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Maritime Spatial Planning Directive Monitoring programme targeting at national legislation OSPAR Coordinated Environmental Monitoring Programme	Maritime Spatial Planning Directive Monitoring programme targeting at national legislation	Maritime Spatial Planning Directive Monitoring programme targeting at national legislation	Maritime Spatial Planning Directive Monitoring programme targeting at national legislation	Maritime Spatial Planning Directive Monitoring programme targeting at national legislation
Regional cooperation - coordinating body										Other	Other	Other	Other	HELCOM Other	HELCOM Other	Other	Other	HELCOM Other	HELCOM Other	HELCOM OSPAR	HELCOM OSPAR	HELCOM OSPAR	HELCOM OSPAR	HELCOM OSPAR	HELCOM OSPAR	HELCOM OSPAR	HELCOM OSPAR	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other
Regional cooperation - countries involved																DE,DK,FI	DE,DK,FI
Regional cooperation - implementation level										Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Joint data collection	Joint data collection	Joint data collection	Joint data collection	Joint data collection	Joint data collection	Joint data collection	Joint data collection	Joint data collection	Joint data collection	Joint data collection	Joint data collection
Monitoring details
Features	Non-renewable energy generation	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Coastal fish	Demersal shelf fish	Pelagic shelf fish	Newly introduced non-indigenous species	Established non-indigenous species	Hydrographical changes	Input of other forms of energy (including electromagnetic fields, light and heat)	Fish and shellfish harvesting (professional, recreational)	Species affected by incidental by-catch	Fish and shellfish harvesting (professional, recreational)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Coastal fish	Coastal fish	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Fish and shellfish harvesting (professional, recreational)	Pelagic shelf fish	Pelagic shelf fish	Coastal fish	Coastal fish	Coastal fish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Coastal ecosystems	Coastal ecosystems	Coastal ecosystems	Demersal shelf fish	Pelagic shelf fish	Demersal shelf fish	Pelagic shelf fish	Demersal shelf fish	Pelagic shelf fish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Shelf ecosystems	Shelf ecosystems	Shelf ecosystems	Coastal fish	Demersal shelf fish	Coastal ecosystems	Adverse effects on species or habitats
Elements			Abramis brama Alburnus alburnus Anguilla anguilla Blicca bjoerkna Ciliata mustela Ctenolabrus rupestris Esox lucius Gadus morhua Gasterosteus aculeatus Gobius niger Gymnocephalus cernua Labrus bergylta Leuciscus idus Neogobius melanostomus Platichthys flesus Rutilus rutilus Sander lucioperca Scardinius erythrophthalmus Symphodus melops Syngnathus acus Tinca tinca Zoarces viviparus	Myoxocephalus scorpius Perca fluviatilis Pleuronectes platessa Syngnathus typhle Taurulus bubalis	Clupea harengus	Not Applicable	Alkmaria romijni Bonnemaisonia hamifera Crassostrea gigas Dasya baillouviana Hemigrapsus sanguineus Marenzelleria spp. (neglecta & viridis) Neogobius melanostomus Oncorhynchus mykiss Potamopyrgus antipodarum Sargassum muticum Spermothamnion repens var. flagelliferum	Temperature	Not Applicable		Not Applicable		Not Applicable	Anguilla anguilla	Anguilla anguilla	Not Applicable	Not Applicable	Salmo salar Salmo trutta trutta	Salmo salar Salmo trutta trutta	Alburnus alburnus Coregonus maraena Ctenolabrus rupestris Gadus morhua Gobius niger Gymnocephalus cernua Osmerus eperlanus Platichthys flesus Rutilus rutilus Sander lucioperca Scardinius erythrophthalmus Symphodus melops Zoarces viviparus	Alburnus alburnus Coregonus maraena Ctenolabrus rupestris Gadus morhua Gobius niger Gymnocephalus cernua Osmerus eperlanus Platichthys flesus Rutilus rutilus Sander lucioperca Scardinius erythrophthalmus Symphodus melops Zoarces viviparus	Alburnus alburnus Coregonus maraena Ctenolabrus rupestris Gadus morhua Gobius niger Gymnocephalus cernua Osmerus eperlanus Platichthys flesus Rutilus rutilus Sander lucioperca Scardinius erythrophthalmus Symphodus melops Zoarces viviparus	Anguilla anguilla Clupea harengus Ctenolabrus rupestris Gadus morhua Limanda limanda Melanogrammus aeglefinus Merlangius merlangus Perca fluviatilis Platichthys flesus Pleuronectes platessa Pollachius virens Rutilus rutilus Sander lucioperca Scophthalmus rhombus Solea solea Symphodus melops	Anguilla anguilla Clupea harengus Ctenolabrus rupestris Gadus morhua Limanda limanda Melanogrammus aeglefinus Merlangius merlangus Perca fluviatilis Platichthys flesus Pleuronectes platessa Pollachius virens Rutilus rutilus Sander lucioperca Scophthalmus rhombus Solea solea Symphodus melops	Fish community	Fish community	Fish community	Amblyraja radiata Anguilla anguilla Argentina silus Coryphaenoides rupestris Dicentrarchus labrax Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Micromesistius poutassou Microstomus kitt Molva molva Phycis blennoides Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja clavata Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea (sin. vulgaris) Trachurus trachurus	Clupea harengus Cyclopterus lumpus Dicentrarchus labrax Scomber scombrus Sprattus sprattus Squalus acanthias	Amblyraja radiata Anguilla anguilla Argentina silus Coryphaenoides rupestris Dicentrarchus labrax Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Micromesistius poutassou Microstomus kitt Molva molva Phycis blennoides Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja clavata Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea (sin. vulgaris) Trachurus trachurus	Clupea harengus Cyclopterus lumpus Dicentrarchus labrax Scomber scombrus Sprattus sprattus Squalus acanthias	Amblyraja radiata Anguilla anguilla Argentina silus Coryphaenoides rupestris Dicentrarchus labrax Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Micromesistius poutassou Microstomus kitt Molva molva Phycis blennoides Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja clavata Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea (sin. vulgaris) Trachurus trachurus	Clupea harengus Cyclopterus lumpus Dicentrarchus labrax Scomber scombrus Sprattus sprattus Squalus acanthias	Amblyraja radiata Ammodytes spp. Anguilla anguilla Argentina silus Cancer pagurus Clupea harengus Coryphaenoides rupestris Dicentrarchus labrax Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Micromesistius poutassou Microstomus kitt Molva molva Nephrops norvegicus Pandalus borealis Phycis blennoides Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja clavata Scomber scombrus Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea Sprattus sprattus Squalus acanthias Trachurus trachurus Trisopterus esmarkii	Amblyraja radiata Ammodytes spp. Anguilla anguilla Argentina silus Cancer pagurus Clupea harengus Coryphaenoides rupestris Dicentrarchus labrax Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Micromesistius poutassou Microstomus kitt Molva molva Nephrops norvegicus Pandalus borealis Phycis blennoides Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja clavata Scomber scombrus Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea Sprattus sprattus Squalus acanthias Trachurus trachurus Trisopterus esmarkii	Amblyraja radiata Ammodytes spp. Anguilla anguilla Argentina silus Cancer pagurus Clupea harengus Coryphaenoides rupestris Dicentrarchus labrax Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Micromesistius poutassou Microstomus kitt Molva molva Nephrops norvegicus Pandalus borealis Phycis blennoides Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja clavata Scomber scombrus Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea Sprattus sprattus Squalus acanthias Trachurus trachurus Trisopterus esmarkii	Fish community	Fish community	Fish community	Zoarces viviparus	Perca fluviatilis	Fish community	Perca fluviatilis Zoarces viviparus
GES criteria			D1C2	D1C2	D1C2	D2C1	D2C2	D7C1	D7C1		D1C1		D3C1	D1C2	D1C4	D3C1	NotRelevan	D1C2	D1C4	D1C2	D1C3	D1C4	D3C2	D3C3	D4C1	D4C2	D4C3	D1C2	D1C2	D1C3	D1C3	D1C4	D1C4	D3C1	D3C2	D3C3	D4C1	D4C2	D4C3	D1C3	D1C3	D4C4	D8C2
Parameters			Abundance (number of individuals) Biomass Other	Abundance (number of individuals) Biomass	Abundance (number of individuals) Biomass	Presence	Abundance (number of individuals) Biomass	Extent	Other		Mortality (weight/volume; number of individuals)		Mortality (weight/volume; number of individuals)	Abundance (number of individuals) Biomass Other	Distribution (range)	Mortality (weight/volume; number of individuals) Other	Other	Abundance (number of individuals) Biomass Other	Distribution (range)	Abundance (number of individuals) Biomass	Age distribution Other Sex distribution	Distribution (range) Distribution (spatial)	Abundance (number of individuals) Biomass of Spawning Stock (SSB)	Length Other Size distribution	Other	Abundance (number of individuals) Biomass	Size distribution	Abundance (number of individuals) Biomass	Abundance (number of individuals) Biomass	Age distribution Length Other Sex distribution	Age distribution Length Other Sex distribution	Distribution (range)	Distribution (range)	Mortality (weight/volume; number of individuals)	Abundance (number of individuals) Biomass of Spawning Stock (SSB)	Length Size distribution	Other	Abundance (number of individuals) Biomass	Size distribution	Age distribution Length Other	Age distribution Length Other	Other	Other
Parameter Other			Size distribution						temperature					Length Mass Age distribution Lifestage Stage of ma		Species composition, Size distribution, and Inform	Information regarding the fisherman, fishing metho	Age distribution Lifestage Presence of parasites (			Developmental state of gonads Presence of parasite			Mass	Species composition					Mass Size distribution Developmental state of gona	Mass Size distribution Developmental state of gona						Species composition			Mass	Mass	Age distribution Mass Length	Visual inspection of external and internal defects
Spatial scope	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)
Marine reporting units	ANS-SE-AA-B_Kattegatt BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund	ANS-SE-AA-BG_Vasterhavet BAL-SE-AA-BG_Bottniska_Viken BAL-SE-AA-BG_Egentliga_Ostersjon	ANS-SE-AA-BG_Vasterhavet BAL-SE-AA-BG_Bottniska_Viken BAL-SE-AA-BG_Egentliga_Ostersjon	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Oresund ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Alands_hav BAL-SE-AA-B_Arkonahavet_och_S_Oresund BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_Bottenviken BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_N_Gotlandshavet BAL-SE-AA-B_O_Gotlandshavet BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_V_Gotlandshavet	ANS-SE-AA-B_Kattegatt ANS-SE-AA-B_Skagerrak BAL-SE-AA-B_Bornholmshavet_och_Hanobukten BAL-SE-AA-B_Bottenhavet BAL-SE-AA-B_N_Kvarken BAL-SE-AA-B_V_Gotlandshavet
Temporal scope (start date - end date)	1968-9999	1968-9999	1968-9999	1968-9999	1968-9999	1968-9999	1968-9999	1968-9999	1968-9999	1996-9999	1996-9999	1994-9999	1994-9999	1969-9999	1969-9999	1973-9999	1973-9999	2004-9999	2004-9999	1960-9999	1960-9999	1960-9999	1960-9999	1960-9999	1960-9999	1960-9999	1960-9999	1972-9999	1972-9999	1972-9999	1972-9999	1972-9999	1972-9999	1972-9999	1972-9999	1972-9999	1972-9999	1972-9999	1972-9999	1988-9999	1988-9999	1988-9999	1988-9999
Monitoring frequency	Other	Other	Other	Other	Other	Other	Other	Other	Other	3-monthly	3-monthly	Continually	Continually	Yearly	Yearly	Other	Other	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Yearly	Yearly	Yearly	Yearly
Monitoring type	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	Other Visual observation	Other Visual observation	Administrative data collection Other	Administrative data collection Other	In-situ sampling coastal	In-situ sampling coastal	Administrative data collection In-situ sampling coastal Visual observation	Administrative data collection In-situ sampling coastal Visual observation	Administrative data collection In-situ sampling coastal Remote surveillance	Administrative data collection In-situ sampling coastal Remote surveillance	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal
Monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	Other monitoring method	Other monitoring method	NEAFC: Recording of Catch and Fishing Effort Other monitoring method	NEAFC: Recording of Catch and Fishing Effort Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX SISP 7 - BITS Manual for the Baltic International Trawl Surveys	OSPAR JAMP Guidelines for Contaminant-Specific Biological Effects (Agreement 2008-09) (Replaces Agreement 2003-10) OSPAR JAMP Guidelines for General Biological Effects Monitoring. Revised technical annexes 2007 (Agreement 2007-07) Other monitoring method	OSPAR JAMP Guidelines for Contaminant-Specific Biological Effects (Agreement 2008-09) (Replaces Agreement 2003-10) OSPAR JAMP Guidelines for General Biological Effects Monitoring. Revised technical annexes 2007 (Agreement 2007-07) Other monitoring method	OSPAR JAMP Guidelines for Contaminant-Specific Biological Effects (Agreement 2008-09) (Replaces Agreement 2003-10) OSPAR JAMP Guidelines for General Biological Effects Monitoring. Revised technical annexes 2007 (Agreement 2007-07) Other monitoring method	OSPAR JAMP Guidelines for Contaminant-Specific Biological Effects (Agreement 2008-09) (Replaces Agreement 2003-10) OSPAR JAMP Guidelines for General Biological Effects Monitoring. Revised technical annexes 2007 (Agreement 2007-07) Other monitoring method
Monitoring method other	"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"	"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"	"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"	"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"	"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"	"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"	"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"	"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"	"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"	Catches and by-catches are monitored with the help of observers who accompany the fishing vessels during commercial fishing. The regular sampling is divided into area, fisheries and quarters. This means that observations are made every quarter from different types of bottom trawls (shrimp trawl, crayfish trawl with grate, trawl without grate). Usually, in the order of 0.5-2% (different for different types of fisheries) of commercial fishing trips are observed. The fishing trips observed are selected at random. Observations of by-catch within the framework of the pilot studies are carried out in the same manner. The observers examine the entire process during which the fishing gear is hauled so that also by-catches that do not follow on board but fall out of the nets can be registered. Furthermore, the observers examine the entire sorting of the catch. The observers then measure and weigh the catch and take samples for biological analysis. Remote surveillance using cameras onboard is being tested during 2020, and may supplement the monitoring in the future.	Catches and by-catches are monitored with the help of observers who accompany the fishing vessels during commercial fishing. The regular sampling is divided into area, fisheries and quarters. This means that observations are made every quarter from different types of bottom trawls (shrimp trawl, crayfish trawl with grate, trawl without grate). Usually, in the order of 0.5-2% (different for different types of fisheries) of commercial fishing trips are observed. The fishing trips observed are selected at random. Observations of by-catch within the framework of the pilot studies are carried out in the same manner. The observers examine the entire process during which the fishing gear is hauled so that also by-catches that do not follow on board but fall out of the nets can be registered. Furthermore, the observers examine the entire sorting of the catch. The observers then measure and weigh the catch and take samples for biological analysis. Remote surveillance using cameras onboard is being tested during 2020, and may supplement the monitoring in the future.	"https://www.havochvatten.se/fiske-och-handel/rapportering-och-e-tjanster/yrkesfiske/manualer-for-verksamma-inom-yrkesfisket.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/lagstiftning-direktiv-och-forordningar/lagstiftning-som-ror-yrkesfisket.html "	"https://www.havochvatten.se/fiske-och-handel/rapportering-och-e-tjanster/yrkesfiske/manualer-for-verksamma-inom-yrkesfisket.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/lagstiftning-direktiv-och-forordningar/lagstiftning-som-ror-yrkesfisket.html "	Several different methods are used in eel monitoring. In the North Sea, test fishing with eel traps place, similar to the method described in the method standard ”Provfiske med kustöversiktsnät, nätlänkar och ryssjor” on coastal shallow water. In the Baltic Sea, eels are collected through commercial fishing within the framework of DCF. Sampling with stationary trawl takes place in the intake channel of cooling water to Ringhals nuclear power plant and catches glass eels. The method is described in the reports from the Biological recipient control at Ringhals nuclear power plant. By tagging and then recapturing the tagged eel on the Baltic coast, a measure is obtained of how hard the fishing pressure is (ICES report WGEEL 2018).	Several different methods are used in eel monitoring. In the North Sea, test fishing with eel traps place, similar to the method described in the method standard ”Provfiske med kustöversiktsnät, nätlänkar och ryssjor” on coastal shallow water. In the Baltic Sea, eels are collected through commercial fishing within the framework of DCF. Sampling with stationary trawl takes place in the intake channel of cooling water to Ringhals nuclear power plant and catches glass eels. The method is described in the reports from the Biological recipient control at Ringhals nuclear power plant. By tagging and then recapturing the tagged eel on the Baltic coast, a measure is obtained of how hard the fishing pressure is (ICES report WGEEL 2018).	There is currently no method that captures all data in a cost-effective way. Therefore, it is important to choose the right method(s) to answer the questions asked. Data of interest may be of a biological or non-biological nature. Biological data include, for example, the number and sizes of fish caught. Non-biological data can be, for example, different measures of effort, characterization of practitioners and socio-economic aspects. The methods are described separately below, but a preferred data collection is in most cases a combination of the methods to provide a comprehensive knowledge base of the structure of the fishery, participants and their activity and catches, including re-released catches. Depending on which question or questions are to be answered, methods can be combined flexibly. National survey The survey uses a panel design with a stratified random sample. More information regarding the design of the survey is summarized in a quality declaration - https://www.havochvatten.se/download/18.619e9cdf163fb20d0dd815a1/1529477995525/kvalitetsdeklaration-2017.pdf . Site visiting studies Site-visiting studies include, for example, inventories and interviews of recreational fishermen in port or during fishing. Inventories can be made by boat, in port or by plane. The pilot study in the Sound and the Southern Baltic Sea includes several different fishing methods. Therefore, the methodology differs depending on which fishing method is studied. Sampling takes place at random at all landing sites in the area (tour boats, charter boats, private boats and fishing from land) to describe the extent of recreational fishing, the number of fishermen and the amount of fish. More about this project is described here: https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/fritidsfiske/. More information about recreational fishing surveys, its methods and the overall work in Sweden can be read in SLU Aqua's Aqua reports - https://www.slu.se/globalassets/ew/org/inst/aqua/externwebb/sidan-publikationer/aqua-reports-xxxx_xx/aquarapporter/2018/aqua-reports-2018_22.pdf.	There is currently no method that captures all data in a cost-effective way. Therefore, it is important to choose the right method(s) to answer the questions asked. Data of interest may be of a biological or non-biological nature. Biological data include, for example, the number and sizes of fish caught. Non-biological data can be, for example, different measures of effort, characterization of practitioners and socio-economic aspects. The methods are described separately below, but a preferred data collection is in most cases a combination of the methods to provide a comprehensive knowledge base of the structure of the fishery, participants and their activity and catches, including re-released catches. Depending on which question or questions are to be answered, methods can be combined flexibly. National survey The survey uses a panel design with a stratified random sample. More information regarding the design of the survey is summarized in a quality declaration - https://www.havochvatten.se/download/18.619e9cdf163fb20d0dd815a1/1529477995525/kvalitetsdeklaration-2017.pdf . Site visiting studies Site-visiting studies include, for example, inventories and interviews of recreational fishermen in port or during fishing. Inventories can be made by boat, in port or by plane. The pilot study in the Sound and the Southern Baltic Sea includes several different fishing methods. Therefore, the methodology differs depending on which fishing method is studied. Sampling takes place at random at all landing sites in the area (tour boats, charter boats, private boats and fishing from land) to describe the extent of recreational fishing, the number of fishermen and the amount of fish. More about this project is described here: https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/fritidsfiske/. More information about recreational fishing surveys, its methods and the overall work in Sweden can be read in SLU Aqua's Aqua reports - https://www.slu.se/globalassets/ew/org/inst/aqua/externwebb/sidan-publikationer/aqua-reports-xxxx_xx/aquarapporter/2018/aqua-reports-2018_22.pdf.	https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/fisk-i-rinnande-vatten---vadningselfiske.html	https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/fisk-i-rinnande-vatten---vadningselfiske.html	"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."	"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."	"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."	"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."	"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."	"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."	"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."	"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/halsotillstand-hos-kustfisk.html	https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/halsotillstand-hos-kustfisk.html	https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/halsotillstand-hos-kustfisk.html	https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/halsotillstand-hos-kustfisk.html
Quality control	https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/	https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/	https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/	https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/	https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/	https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/	https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/	https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/	https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/	Sampling takes place through a random selection of ships/voyages. The observers bring with them a manual for determining the species of birds and also photograph captured birds as much as possible. Data is registered in the national database Fiskdata2 according to the updated manual. Data is examined and checked in several respects. Quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers).	Sampling takes place through a random selection of ships/voyages. The observers bring with them a manual for determining the species of birds and also photograph captured birds as much as possible. Data is registered in the national database Fiskdata2 according to the updated manual. Data is examined and checked in several respects. Quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers).	Commercial fishing reporting is standardized. The information is validated and checked during physical and administrative control by SwAM and the Coast Guard. Physical inspections are carried out on site on the ships in port by SwAM and at sea by the Swedish Coast Guard. Quality assurance of the economic statistics is carried out according to proven methods and practices.	Commercial fishing reporting is standardized. The information is validated and checked during physical and administrative control by SwAM and the Coast Guard. Physical inspections are carried out on site on the ships in port by SwAM and at sea by the Swedish Coast Guard. Quality assurance of the economic statistics is carried out according to proven methods and practices.	The quality assurance is conducted by strictly following standardized methodology. Quality assurance takes place within the data hosting at SLU. Data is quality assured electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material.	The quality assurance is conducted by strictly following standardized methodology. Quality assurance takes place within the data hosting at SLU. Data is quality assured electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material.	QC of the national survey is summarized in a quality declaration - https://www.havochvatten.se/download/18.619e9cdf163fb20d0dd815a1/1529477995525/kvalitetsdeklaration-2017.pdf . QC of the Site visiting studies is described in the final reports of each projects - https://www.slu.se/globalassets/ew/org/inst/aqua/externwebb/sidan-publikationer/aqua-reports-xxxx_xx/aquarapporter/2018/aqua-reports-2018_22.pdf. The methods carried out on the basis of EU data collection regulations, including the pilot projects, are also evaluated by ICES working group WGRFS.	QC of the national survey is summarized in a quality declaration - https://www.havochvatten.se/download/18.619e9cdf163fb20d0dd815a1/1529477995525/kvalitetsdeklaration-2017.pdf . QC of the Site visiting studies is described in the final reports of each projects - https://www.slu.se/globalassets/ew/org/inst/aqua/externwebb/sidan-publikationer/aqua-reports-xxxx_xx/aquarapporter/2018/aqua-reports-2018_22.pdf. The methods carried out on the basis of EU data collection regulations, including the pilot projects, are also evaluated by ICES working group WGRFS.	Monitoring programmes are coordinated and developed in consultation with ICES Working Groups on Salmon in the Baltic Sea (WGBAST) and the Atlantic (WGNAS) and within the EU RCG. The programmes are evaluated by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). In connection with the data being entered into the database, they undergo a quality check. The QC includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Results from electric fishing are reported in digital field protocols that are quality assured in SLU's database Swedish Electricity Fishing Registers (SERS). Quality assurance of age determination (via scales) takes place through recurring international calibrations.	Monitoring programmes are coordinated and developed in consultation with ICES Working Groups on Salmon in the Baltic Sea (WGBAST) and the Atlantic (WGNAS) and within the EU RCG. The programmes are evaluated by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). In connection with the data being entered into the database, they undergo a quality check. The QC includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Results from electric fishing are reported in digital field protocols that are quality assured in SLU's database Swedish Electricity Fishing Registers (SERS). Quality assurance of age determination (via scales) takes place through recurring international calibrations.	The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf	The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf	The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf	The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf	The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf	The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf	The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf	The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	For monitoring the health condition of coastal fish, there is a quality declaration that includes the organization, division of responsibilities and quality routines for the monitoring activities. Capture, sampling procedures, analyzes (biochemical, physiological, histological and pathological measurement variables) and data management take place in a standardized manner and follow prepared method instructions. Most of the sampling routines and analysis methods included in the method standard ”Hälsotillstånd hos kustfisk” are covered by accreditation by Swedac.	For monitoring the health condition of coastal fish, there is a quality declaration that includes the organization, division of responsibilities and quality routines for the monitoring activities. Capture, sampling procedures, analyzes (biochemical, physiological, histological and pathological measurement variables) and data management take place in a standardized manner and follow prepared method instructions. Most of the sampling routines and analysis methods included in the method standard ”Hälsotillstånd hos kustfisk” are covered by accreditation by Swedac.	For monitoring the health condition of coastal fish, there is a quality declaration that includes the organization, division of responsibilities and quality routines for the monitoring activities. Capture, sampling procedures, analyzes (biochemical, physiological, histological and pathological measurement variables) and data management take place in a standardized manner and follow prepared method instructions. Most of the sampling routines and analysis methods included in the method standard ”Hälsotillstånd hos kustfisk” are covered by accreditation by Swedac.	For monitoring the health condition of coastal fish, there is a quality declaration that includes the organization, division of responsibilities and quality routines for the monitoring activities. Capture, sampling procedures, analyzes (biochemical, physiological, histological and pathological measurement variables) and data management take place in a standardized manner and follow prepared method instructions. Most of the sampling routines and analysis methods included in the method standard ”Hälsotillstånd hos kustfisk” are covered by accreditation by Swedac.
Data management	The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se	The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se	The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se	The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se	The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se	The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se	The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se	The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se	The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se			On SwAM's website, you can freely search for available data on catch statistics for commercial fishing and daily fishing. Financial data are presented annually in the Annual Economic Reports.	On SwAM's website, you can freely search for available data on catch statistics for commercial fishing and daily fishing. Financial data are presented annually in the Annual Economic Reports.					Electricity fishing data is stored and made publicly accessible via the Electricity Fisheries Register. Raw data from smolt traps are stored in ”Sötebasen” (database under construction at SLU Aqua). There is no national database for fish counters yet. Other information collected is stored in smaller databases at SLU Aqua, from which data can be obtained on request. Swedish data used internationally is delivered to relevant working groups within ICES. Aggregated data from commercial fishing for salmon are stored in ICES database InterCatch.	Electricity fishing data is stored and made publicly accessible via the Electricity Fisheries Register. Raw data from smolt traps are stored in ”Sötebasen” (database under construction at SLU Aqua). There is no national database for fish counters yet. Other information collected is stored in smaller databases at SLU Aqua, from which data can be obtained on request. Swedish data used internationally is delivered to relevant working groups within ICES. Aggregated data from commercial fishing for salmon are stored in ICES database InterCatch.	The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.	The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.	The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.	The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.	The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.	The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.	The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.	The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.
Data access	https://www.havochvatten.se/marin-miljoovervakning-kylvatten-data	https://www.havochvatten.se/marin-miljoovervakning-kylvatten-data	https://www.havochvatten.se/marin-miljoovervakning-kylvatten-data	https://www.havochvatten.se/marin-miljoovervakning-kylvatten-data	https://www.havochvatten.se/marin-miljoovervakning-kylvatten-data	https://www.havochvatten.se/marin-miljoovervakning-kylvatten-data	https://www.havochvatten.se/marin-miljoovervakning-kylvatten-data	https://www.havochvatten.se/marin-miljoovervakning-kylvatten-data	https://www.havochvatten.se/marin-miljoovervakning-kylvatten-data	https://www.havochvatten.se/marin-miljoovervakning-bifangst-data	https://www.havochvatten.se/marin-miljoovervakning-bifangst-data	https://www.havochvatten.se/marin-miljoovervakning-kontroll-fiskeriverksamhet-data	https://www.havochvatten.se/marin-miljoovervakning-kontroll-fiskeriverksamhet-data	https://www.slu.se/institutioner/akvatiska-resurser/databaser/kul/	https://www.slu.se/institutioner/akvatiska-resurser/databaser/kul/	https://www.havochvatten.se/marin-miljoovervakning-fritidsfiske-data	https://www.havochvatten.se/marin-miljoovervakning-fritidsfiske-data	https://www.havochvatten.se/marin-miljoovervakning-migrerande-lax-data	https://www.havochvatten.se/marin-miljoovervakning-migrerande-lax-data	https://www.havochvatten.se/marin-miljoovervakning-kustfisk-data	https://www.havochvatten.se/marin-miljoovervakning-kustfisk-data	https://www.havochvatten.se/marin-miljoovervakning-kustfisk-data	https://www.havochvatten.se/marin-miljoovervakning-kustfisk-data	https://www.havochvatten.se/marin-miljoovervakning-kustfisk-data	https://www.havochvatten.se/marin-miljoovervakning-kustfisk-data	https://www.havochvatten.se/marin-miljoovervakning-kustfisk-data	https://www.havochvatten.se/marin-miljoovervakning-kustfisk-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/provfisken/provfiske-vid-kusten/nationell-miljoovervakning-integrerad-fiskovervakning/	https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/provfisken/provfiske-vid-kusten/nationell-miljoovervakning-integrerad-fiskovervakning/	https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/provfisken/provfiske-vid-kusten/nationell-miljoovervakning-integrerad-fiskovervakning/	https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/provfisken/provfiske-vid-kusten/nationell-miljoovervakning-integrerad-fiskovervakning/
Related indicator/name	ANSSE-2.1A_Intro_fr�mmande_art ANSSE-C.1.1_Intro_fr�mmande_art BALSE-2.1A_Intro_fr�mmande_art BALSE-C.1.1_Intro_fr�mmande_art	ANSSE-2.1A_Intro_fr�mmande_art ANSSE-C.1.1_Intro_fr�mmande_art BALSE-2.1A_Intro_fr�mmande_art BALSE-C.1.1_Intro_fr�mmande_art	ANSSE-2.1A_Intro_fr�mmande_art ANSSE-C.1.1_Intro_fr�mmande_art BALSE-2.1A_Intro_fr�mmande_art BALSE-C.1.1_Intro_fr�mmande_art	ANSSE-2.1A_Intro_fr�mmande_art ANSSE-C.1.1_Intro_fr�mmande_art BALSE-2.1A_Intro_fr�mmande_art BALSE-C.1.1_Intro_fr�mmande_art	ANSSE-2.1A_Intro_fr�mmande_art ANSSE-C.1.1_Intro_fr�mmande_art BALSE-2.1A_Intro_fr�mmande_art BALSE-C.1.1_Intro_fr�mmande_art	ANSSE-2.1A_Intro_fr�mmande_art ANSSE-C.1.1_Intro_fr�mmande_art BALSE-2.1A_Intro_fr�mmande_art BALSE-C.1.1_Intro_fr�mmande_art	ANSSE-2.1A_Intro_fr�mmande_art ANSSE-C.1.1_Intro_fr�mmande_art BALSE-2.1A_Intro_fr�mmande_art BALSE-C.1.1_Intro_fr�mmande_art	ANSSE-2.1A_Intro_fr�mmande_art ANSSE-C.1.1_Intro_fr�mmande_art BALSE-2.1A_Intro_fr�mmande_art BALSE-C.1.1_Intro_fr�mmande_art	ANSSE-2.1A_Intro_fr�mmande_art ANSSE-C.1.1_Intro_fr�mmande_art BALSE-2.1A_Intro_fr�mmande_art BALSE-C.1.1_Intro_fr�mmande_art	BALSE-1.1A_Bif�ngst_tumlare	BALSE-1.1A_Bif�ngst_tumlare	ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.1_Fiskerid�dlighet BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.1_Fiskerid�dlighet	ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.1_Fiskerid�dlighet BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.1_Fiskerid�dlighet	ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.3_H�llbart_nyttjande_arter	ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.3_H�llbart_nyttjande_arter	ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.1_Fiskerid�dlighet BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.1_Fiskerid�dlighet	ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.1_Fiskerid�dlighet BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.1_Fiskerid�dlighet			1.2F Förekomst av nyckelart av fisk i kustvatten – abborre och skrubbskädda/ 1.2F Abundance of key fish species in coastal waters - perch and flounder 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 4.2A Abundans av viktiga funktionella grupper av fisk i kustvatten - rovfisk och karpfisk/ 4.2A Abundance of important functional fish groups in coastal waters C.4.2 Storleksstruktur hos nyckelart i kustvatten - torsk/ C.4.2 Size structure in key fish species in coastal waters – cod C.4.3 Storleksstruktur hos nyckelart av fisk i kustvatten – abborre / C.4.3 Size structure in key fish species in coastal waters - perch 1.2G Förekomst av nyckelart av fisk i kustvatten – abundans av stor torsk/ 1.2G Abundance of key fish species in coastal waters - large cod 1.3C Andel stor bottenlevande fisk i fjord- och skärgårdsområden/ 1.3C Proportion of large demersal fish (LFI) in fjord and archipelago areas ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter	1.2F Förekomst av nyckelart av fisk i kustvatten – abborre och skrubbskädda/ 1.2F Abundance of key fish species in coastal waters - perch and flounder 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 4.2A Abundans av viktiga funktionella grupper av fisk i kustvatten - rovfisk och karpfisk/ 4.2A Abundance of important functional fish groups in coastal waters C.4.2 Storleksstruktur hos nyckelart i kustvatten - torsk/ C.4.2 Size structure in key fish species in coastal waters – cod C.4.3 Storleksstruktur hos nyckelart av fisk i kustvatten – abborre / C.4.3 Size structure in key fish species in coastal waters - perch 1.2G Förekomst av nyckelart av fisk i kustvatten – abundans av stor torsk/ 1.2G Abundance of key fish species in coastal waters - large cod 1.3C Andel stor bottenlevande fisk i fjord- och skärgårdsområden/ 1.3C Proportion of large demersal fish (LFI) in fjord and archipelago areas ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter	1.2F Förekomst av nyckelart av fisk i kustvatten – abborre och skrubbskädda/ 1.2F Abundance of key fish species in coastal waters - perch and flounder 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 4.2A Abundans av viktiga funktionella grupper av fisk i kustvatten - rovfisk och karpfisk/ 4.2A Abundance of important functional fish groups in coastal waters C.4.2 Storleksstruktur hos nyckelart i kustvatten - torsk/ C.4.2 Size structure in key fish species in coastal waters – cod C.4.3 Storleksstruktur hos nyckelart av fisk i kustvatten – abborre / C.4.3 Size structure in key fish species in coastal waters - perch 1.2G Förekomst av nyckelart av fisk i kustvatten – abundans av stor torsk/ 1.2G Abundance of key fish species in coastal waters - large cod 1.3C Andel stor bottenlevande fisk i fjord- och skärgårdsområden/ 1.3C Proportion of large demersal fish (LFI) in fjord and archipelago areas ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter	1.2F Förekomst av nyckelart av fisk i kustvatten – abborre och skrubbskädda/ 1.2F Abundance of key fish species in coastal waters - perch and flounder 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 4.2A Abundans av viktiga funktionella grupper av fisk i kustvatten - rovfisk och karpfisk/ 4.2A Abundance of important functional fish groups in coastal waters C.4.2 Storleksstruktur hos nyckelart i kustvatten - torsk/ C.4.2 Size structure in key fish species in coastal waters – cod C.4.3 Storleksstruktur hos nyckelart av fisk i kustvatten – abborre / C.4.3 Size structure in key fish species in coastal waters - perch 1.2G Förekomst av nyckelart av fisk i kustvatten – abundans av stor torsk/ 1.2G Abundance of key fish species in coastal waters - large cod 1.3C Andel stor bottenlevande fisk i fjord- och skärgårdsområden/ 1.3C Proportion of large demersal fish (LFI) in fjord and archipelago areas ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter	1.2F Förekomst av nyckelart av fisk i kustvatten – abborre och skrubbskädda/ 1.2F Abundance of key fish species in coastal waters - perch and flounder 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 4.2A Abundans av viktiga funktionella grupper av fisk i kustvatten - rovfisk och karpfisk/ 4.2A Abundance of important functional fish groups in coastal waters C.4.2 Storleksstruktur hos nyckelart i kustvatten - torsk/ C.4.2 Size structure in key fish species in coastal waters – cod C.4.3 Storleksstruktur hos nyckelart av fisk i kustvatten – abborre / C.4.3 Size structure in key fish species in coastal waters - perch 1.2G Förekomst av nyckelart av fisk i kustvatten – abundans av stor torsk/ 1.2G Abundance of key fish species in coastal waters - large cod 1.3C Andel stor bottenlevande fisk i fjord- och skärgårdsområden/ 1.3C Proportion of large demersal fish (LFI) in fjord and archipelago areas ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter	1.2F Förekomst av nyckelart av fisk i kustvatten – abborre och skrubbskädda/ 1.2F Abundance of key fish species in coastal waters - perch and flounder 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 4.2A Abundans av viktiga funktionella grupper av fisk i kustvatten - rovfisk och karpfisk/ 4.2A Abundance of important functional fish groups in coastal waters C.4.2 Storleksstruktur hos nyckelart i kustvatten - torsk/ C.4.2 Size structure in key fish species in coastal waters – cod C.4.3 Storleksstruktur hos nyckelart av fisk i kustvatten – abborre / C.4.3 Size structure in key fish species in coastal waters - perch 1.2G Förekomst av nyckelart av fisk i kustvatten – abundans av stor torsk/ 1.2G Abundance of key fish species in coastal waters - large cod 1.3C Andel stor bottenlevande fisk i fjord- och skärgårdsområden/ 1.3C Proportion of large demersal fish (LFI) in fjord and archipelago areas ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter	1.2F Förekomst av nyckelart av fisk i kustvatten – abborre och skrubbskädda/ 1.2F Abundance of key fish species in coastal waters - perch and flounder 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 4.2A Abundans av viktiga funktionella grupper av fisk i kustvatten - rovfisk och karpfisk/ 4.2A Abundance of important functional fish groups in coastal waters C.4.2 Storleksstruktur hos nyckelart i kustvatten - torsk/ C.4.2 Size structure in key fish species in coastal waters – cod C.4.3 Storleksstruktur hos nyckelart av fisk i kustvatten – abborre / C.4.3 Size structure in key fish species in coastal waters - perch 1.2G Förekomst av nyckelart av fisk i kustvatten – abundans av stor torsk/ 1.2G Abundance of key fish species in coastal waters - large cod 1.3C Andel stor bottenlevande fisk i fjord- och skärgårdsområden/ 1.3C Proportion of large demersal fish (LFI) in fjord and archipelago areas ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter	1.2F Förekomst av nyckelart av fisk i kustvatten – abborre och skrubbskädda/ 1.2F Abundance of key fish species in coastal waters - perch and flounder 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 4.2A Abundans av viktiga funktionella grupper av fisk i kustvatten - rovfisk och karpfisk/ 4.2A Abundance of important functional fish groups in coastal waters C.4.2 Storleksstruktur hos nyckelart i kustvatten - torsk/ C.4.2 Size structure in key fish species in coastal waters – cod C.4.3 Storleksstruktur hos nyckelart av fisk i kustvatten – abborre / C.4.3 Size structure in key fish species in coastal waters - perch 1.2G Förekomst av nyckelart av fisk i kustvatten – abundans av stor torsk/ 1.2G Abundance of key fish species in coastal waters - large cod 1.3C Andel stor bottenlevande fisk i fjord- och skärgårdsområden/ 1.3C Proportion of large demersal fish (LFI) in fjord and archipelago areas ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�	ANSSE-8.2D_Reproduktion_t�nglake BALSE-8.2D_Reproduktion_t�nglake	ANSSE-8.2D_Reproduktion_t�nglake BALSE-8.2D_Reproduktion_t�nglake	ANSSE-8.2D_Reproduktion_t�nglake BALSE-8.2D_Reproduktion_t�nglake	ANSSE-8.2D_Reproduktion_t�nglake BALSE-8.2D_Reproduktion_t�nglake
Contact	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se	miljoovervakning@havochvatten.se
References	https://www.havochvatten.se/marin-miljoovervakning-kylvatten	https://www.havochvatten.se/marin-miljoovervakning-kylvatten	https://www.havochvatten.se/marin-miljoovervakning-kylvatten	https://www.havochvatten.se/marin-miljoovervakning-kylvatten	https://www.havochvatten.se/marin-miljoovervakning-kylvatten	https://www.havochvatten.se/marin-miljoovervakning-kylvatten	https://www.havochvatten.se/marin-miljoovervakning-kylvatten	https://www.havochvatten.se/marin-miljoovervakning-kylvatten	https://www.havochvatten.se/marin-miljoovervakning-kylvatten	https://www.havochvatten.se/marin-miljoovervakning-bifangst	https://www.havochvatten.se/marin-miljoovervakning-bifangst	https://www.havochvatten.se/marin-miljoovervakning-kontroll-fiskeriverksamhet	https://www.havochvatten.se/marin-miljoovervakning-kontroll-fiskeriverksamhet	https://www.havochvatten.se/marin-miljoovervakning-migrerande-al	https://www.havochvatten.se/marin-miljoovervakning-migrerande-al	https://www.havochvatten.se/marin-miljoovervakning-fritidsfiske	https://www.havochvatten.se/marin-miljoovervakning-fritidsfiske	https://www.havochvatten.se/marin-miljoovervakning-migrerande-lax	https://www.havochvatten.se/marin-miljoovervakning-migrerande-lax	https://www.havochvatten.se/marin-miljoovervakning-kustfisk	https://www.havochvatten.se/marin-miljoovervakning-kustfisk	https://www.havochvatten.se/marin-miljoovervakning-kustfisk	https://www.havochvatten.se/marin-miljoovervakning-kustfisk	https://www.havochvatten.se/marin-miljoovervakning-kustfisk	https://www.havochvatten.se/marin-miljoovervakning-kustfisk	https://www.havochvatten.se/marin-miljoovervakning-kustfisk	https://www.havochvatten.se/marin-miljoovervakning-kustfisk	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-halsa-fisk	https://www.havochvatten.se/marin-miljoovervakning-halsa-fisk	https://www.havochvatten.se/marin-miljoovervakning-halsa-fisk	https://www.havochvatten.se/marin-miljoovervakning-halsa-fisk