Member State report / Art11 / 2020 / D3 / Sweden / NE Atlantic: Greater North 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 | D3 Commercial fish and shellfish |
| Member State | Sweden |
| Region/subregion | NE Atlantic: Greater North Sea |
| Reported by | Swedish Agency for Marine and Water Management Gullbergs Strandgata 15, 411 04 Göteborg Box 11930, |
| Report date | 2020-10-16 |
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Monitoring strategy description |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. 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.
Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon) |
Coverage of GES criteria |
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 |
Gaps and plans |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1). |
Related targets |
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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 |
Related measures |
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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 |
Related monitoring programmes |
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Programme code |
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-D1D3D4D6-seafloormegafauna |
SE-D1D3D4D6-seafloormegafauna |
SE-D1D3D4D6-seafloormegafauna |
SE-D1D3D4D6-seafloormegafauna |
SE-D1D3D4D6-seafloormegafauna |
SE-D1D3D4D6-seafloormegafauna |
SE-D1D3D4D6-seafloormegafauna |
Programme name |
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 |
Macrozoobenthos - on the seafloor |
Macrozoobenthos - on the seafloor |
Macrozoobenthos - on the seafloor |
Macrozoobenthos - on the seafloor |
Macrozoobenthos - on the seafloor |
Macrozoobenthos - on the seafloor |
Macrozoobenthos - on the seafloor |
Update type |
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 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Old programme codes |
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Programme description |
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. |
What is currently included in the targeted monitoring is the ten-legged crustacean Nephrops norvegicus. The species is nocturnal and lives on and buried in solid clay bottoms. Along the coast of Sweden, the species occur in the Kattegat and Skagerrak. Nephrops norvegicus is an important commercial species that is fished through bottom trawling. In addition to Nephrops norvegicus, other species that live in the same habitat, such as sea pens and other coral animals, can be injured or die as a result of trawling. The purpose of monitoring Nephrops norvegicus is to map the abundance of the species in areas that are fished. This is done in a UWTV survey (Under Water TV), ie by filming the seabed with an underwater camera and counting the number of inhabited holes per unit area. During the monitoring, the effects of trawling can also be assessed.
The geographical coverage of the monitoring is based on the main catchment areas and is thus expected to cover the species main distribution areas. Data collection (in accordance with EU legislation (EU) 2017/1004, (EU) 2019/909 and (EU) 2019/910) through UWTV is coordinated by ICES's working group WGNEPS between several countries in the North Sea area. |
What is currently included in the targeted monitoring is the ten-legged crustacean Nephrops norvegicus. The species is nocturnal and lives on and buried in solid clay bottoms. Along the coast of Sweden, the species occur in the Kattegat and Skagerrak. Nephrops norvegicus is an important commercial species that is fished through bottom trawling. In addition to Nephrops norvegicus, other species that live in the same habitat, such as sea pens and other coral animals, can be injured or die as a result of trawling. The purpose of monitoring Nephrops norvegicus is to map the abundance of the species in areas that are fished. This is done in a UWTV survey (Under Water TV), ie by filming the seabed with an underwater camera and counting the number of inhabited holes per unit area. During the monitoring, the effects of trawling can also be assessed.
The geographical coverage of the monitoring is based on the main catchment areas and is thus expected to cover the species main distribution areas. Data collection (in accordance with EU legislation (EU) 2017/1004, (EU) 2019/909 and (EU) 2019/910) through UWTV is coordinated by ICES's working group WGNEPS between several countries in the North Sea area. |
What is currently included in the targeted monitoring is the ten-legged crustacean Nephrops norvegicus. The species is nocturnal and lives on and buried in solid clay bottoms. Along the coast of Sweden, the species occur in the Kattegat and Skagerrak. Nephrops norvegicus is an important commercial species that is fished through bottom trawling. In addition to Nephrops norvegicus, other species that live in the same habitat, such as sea pens and other coral animals, can be injured or die as a result of trawling. The purpose of monitoring Nephrops norvegicus is to map the abundance of the species in areas that are fished. This is done in a UWTV survey (Under Water TV), ie by filming the seabed with an underwater camera and counting the number of inhabited holes per unit area. During the monitoring, the effects of trawling can also be assessed.
The geographical coverage of the monitoring is based on the main catchment areas and is thus expected to cover the species main distribution areas. Data collection (in accordance with EU legislation (EU) 2017/1004, (EU) 2019/909 and (EU) 2019/910) through UWTV is coordinated by ICES's working group WGNEPS between several countries in the North Sea area. |
What is currently included in the targeted monitoring is the ten-legged crustacean Nephrops norvegicus. The species is nocturnal and lives on and buried in solid clay bottoms. Along the coast of Sweden, the species occur in the Kattegat and Skagerrak. Nephrops norvegicus is an important commercial species that is fished through bottom trawling. In addition to Nephrops norvegicus, other species that live in the same habitat, such as sea pens and other coral animals, can be injured or die as a result of trawling. The purpose of monitoring Nephrops norvegicus is to map the abundance of the species in areas that are fished. This is done in a UWTV survey (Under Water TV), ie by filming the seabed with an underwater camera and counting the number of inhabited holes per unit area. During the monitoring, the effects of trawling can also be assessed.
The geographical coverage of the monitoring is based on the main catchment areas and is thus expected to cover the species main distribution areas. Data collection (in accordance with EU legislation (EU) 2017/1004, (EU) 2019/909 and (EU) 2019/910) through UWTV is coordinated by ICES's working group WGNEPS between several countries in the North Sea area. |
What is currently included in the targeted monitoring is the ten-legged crustacean Nephrops norvegicus. The species is nocturnal and lives on and buried in solid clay bottoms. Along the coast of Sweden, the species occur in the Kattegat and Skagerrak. Nephrops norvegicus is an important commercial species that is fished through bottom trawling. In addition to Nephrops norvegicus, other species that live in the same habitat, such as sea pens and other coral animals, can be injured or die as a result of trawling. The purpose of monitoring Nephrops norvegicus is to map the abundance of the species in areas that are fished. This is done in a UWTV survey (Under Water TV), ie by filming the seabed with an underwater camera and counting the number of inhabited holes per unit area. During the monitoring, the effects of trawling can also be assessed.
The geographical coverage of the monitoring is based on the main catchment areas and is thus expected to cover the species main distribution areas. Data collection (in accordance with EU legislation (EU) 2017/1004, (EU) 2019/909 and (EU) 2019/910) through UWTV is coordinated by ICES's working group WGNEPS between several countries in the North Sea area. |
What is currently included in the targeted monitoring is the ten-legged crustacean Nephrops norvegicus. The species is nocturnal and lives on and buried in solid clay bottoms. Along the coast of Sweden, the species occur in the Kattegat and Skagerrak. Nephrops norvegicus is an important commercial species that is fished through bottom trawling. In addition to Nephrops norvegicus, other species that live in the same habitat, such as sea pens and other coral animals, can be injured or die as a result of trawling. The purpose of monitoring Nephrops norvegicus is to map the abundance of the species in areas that are fished. This is done in a UWTV survey (Under Water TV), ie by filming the seabed with an underwater camera and counting the number of inhabited holes per unit area. During the monitoring, the effects of trawling can also be assessed.
The geographical coverage of the monitoring is based on the main catchment areas and is thus expected to cover the species main distribution areas. Data collection (in accordance with EU legislation (EU) 2017/1004, (EU) 2019/909 and (EU) 2019/910) through UWTV is coordinated by ICES's working group WGNEPS between several countries in the North Sea area. |
What is currently included in the targeted monitoring is the ten-legged crustacean Nephrops norvegicus. The species is nocturnal and lives on and buried in solid clay bottoms. Along the coast of Sweden, the species occur in the Kattegat and Skagerrak. Nephrops norvegicus is an important commercial species that is fished through bottom trawling. In addition to Nephrops norvegicus, other species that live in the same habitat, such as sea pens and other coral animals, can be injured or die as a result of trawling. The purpose of monitoring Nephrops norvegicus is to map the abundance of the species in areas that are fished. This is done in a UWTV survey (Under Water TV), ie by filming the seabed with an underwater camera and counting the number of inhabited holes per unit area. During the monitoring, the effects of trawling can also be assessed.
The geographical coverage of the monitoring is based on the main catchment areas and is thus expected to cover the species main distribution areas. Data collection (in accordance with EU legislation (EU) 2017/1004, (EU) 2019/909 and (EU) 2019/910) through UWTV is coordinated by ICES's working group WGNEPS between several countries in the North Sea area. |
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Regional cooperation - coordinating body |
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Regional cooperation - countries involved |
DE,DK,FI |
DE,DK,FI |
DK |
DK |
DK |
DK |
DK |
DK |
DK |
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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 |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Monitoring details |
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Features |
Fish and shellfish harvesting (professional, recreational)
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Species affected by incidental by-catch
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Fish and shellfish harvesting (professional, recreational)
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Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
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Coastal fish
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Coastal fish
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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
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Pelagic shelf fish
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Coastal fish
|
Coastal fish
|
Coastal fish
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Commercially exploited fish and shellfish
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Commercially exploited fish and shellfish
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Coastal ecosystems
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Coastal ecosystems
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Coastal ecosystems
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Demersal shelf fish
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Pelagic shelf fish
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Demersal shelf fish
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Pelagic shelf fish
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Demersal shelf fish
|
Pelagic shelf fish
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Commercially exploited fish and shellfish
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Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Shelf ecosystems
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Shelf ecosystems
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Shelf ecosystems
|
Commercially exploited fish and shellfish
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Commercially exploited fish and shellfish
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Coastal ecosystems
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Shelf ecosystems
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Coastal ecosystems
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Shelf ecosystems
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Benthic broad habitats
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Elements |
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GES criteria |
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 |
D3C2 |
D3C3 |
D4C2 |
D4C2 |
D4C3 |
D4C3 |
D6C5 |
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Parameters |
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Parameter Other |
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 |
Age distribution Sex distribution |
Age distribution Sex distribution |
Age distribution Sex distribution |
Abundance (number of individuals) Size distributio |
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Spatial scope |
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Marine reporting units |
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Temporal scope (start date - end date) |
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 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
Monitoring frequency |
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 |
Yearly |
Yearly |
Yearly |
Monitoring type |
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Monitoring method |
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Monitoring method other |
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.ices.dk/sites/pub/Publication%20Reports/Cooperative%20Research%20Report%20(CRR)/CRR340.pdf |
https://www.ices.dk/sites/pub/Publication%20Reports/Cooperative%20Research%20Report%20(CRR)/CRR340.pdf |
https://www.ices.dk/sites/pub/Publication%20Reports/Cooperative%20Research%20Report%20(CRR)/CRR340.pdf |
https://www.ices.dk/sites/pub/Publication%20Reports/Cooperative%20Research%20Report%20(CRR)/CRR340.pdf |
https://www.ices.dk/sites/pub/Publication%20Reports/Cooperative%20Research%20Report%20(CRR)/CRR340.pdf |
https://www.ices.dk/sites/pub/Publication%20Reports/Cooperative%20Research%20Report%20(CRR)/CRR340.pdf |
https://www.ices.dk/sites/pub/Publication%20Reports/Cooperative%20Research%20Report%20(CRR)/CRR340.pdf |
Quality control |
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. |
ICES data center data type guidelines and reference images are used for quality assurance. Linns CCC is used as quality control of data to check that the counting is consistent between stations. |
ICES data center data type guidelines and reference images are used for quality assurance. Linns CCC is used as quality control of data to check that the counting is consistent between stations. |
ICES data center data type guidelines and reference images are used for quality assurance. Linns CCC is used as quality control of data to check that the counting is consistent between stations. |
ICES data center data type guidelines and reference images are used for quality assurance. Linns CCC is used as quality control of data to check that the counting is consistent between stations. |
ICES data center data type guidelines and reference images are used for quality assurance. Linns CCC is used as quality control of data to check that the counting is consistent between stations. |
ICES data center data type guidelines and reference images are used for quality assurance. Linns CCC is used as quality control of data to check that the counting is consistent between stations. |
ICES data center data type guidelines and reference images are used for quality assurance. Linns CCC is used as quality control of data to check that the counting is consistent between stations. |
Data management |
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. |
Raw data is stored at SLU Aqua. This data is updated annually and aggregated data is made available upon request. Common international data is stored at ICES |
Raw data is stored at SLU Aqua. This data is updated annually and aggregated data is made available upon request. Common international data is stored at ICES |
Raw data is stored at SLU Aqua. This data is updated annually and aggregated data is made available upon request. Common international data is stored at ICES |
Raw data is stored at SLU Aqua. This data is updated annually and aggregated data is made available upon request. Common international data is stored at ICES |
Raw data is stored at SLU Aqua. This data is updated annually and aggregated data is made available upon request. Common international data is stored at ICES |
Raw data is stored at SLU Aqua. This data is updated annually and aggregated data is made available upon request. Common international data is stored at ICES |
Raw data is stored at SLU Aqua. This data is updated annually and aggregated data is made available upon request. Common international data is stored at ICES |
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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 |
References |