Member State report / Art11 / 2014-2020 / D1-F / 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 2014-10-15; 2020-10-15
GES Descriptor D1 Fish
Member State Sweden
Region/subregion NE Atlantic: Greater North Sea
Reported by Swedish Agency for Marine and Water Management
Report date 2014-10-31; 2020-10-16
Report access
2014 data
2020 data
Monitoring programme Monitoring programme name
MP_D1_4_6_Birds
MP_D1_4_6_Birds
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D3
MP_D3
MP_D3
MP_D3
MP_D3
MP_D3
MP_D3
MP_D3
Monitoring programme Reference existing programme
Monitoring programme Marine Unit ID
Q4e - Programme ID
ANSSE-Birds-D14
ANSSE-Birds-D14
ANSSE-FISH-D14
ANSSE-FISH-D14
ANSSE-FISH-D14
ANSSE-FISH-D14
ANSSE-FISH-D14
ANSSE-FISH-D14
ANSSE-FISH-D14
ANSSE-FISH-D14
ANSSE-mammals-D14
ANSSE-mammals-D14
ANSSE-mammals-D14
ANSSE-mammals-D14
ANSSE-mammals-D14
ANSSE-mammals-D14
ANSSE-COMFISH-D3
ANSSE-COMFISH-D3
ANSSE-COMFISH-D3
ANSSE-COMFISH-D3
ANSSE-COMFISH-D3
ANSSE-COMFISH-D3
ANSSE-COMFISH-D3
ANSSE-COMFISH-D3
Q4f - Programme description
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
Q5e - Natural variability
  • ExpertOpinion
  • ExpertOpinion
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • ExpertOpinion
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
Q5d - Adequacy for assessment of GES Q5d - Adequate data
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
N
Q5d - Adequacy for assessment of GES Q5d - Established methods
N
N
Y
Y
Y
Y
Y
Y
Y
Y
N
N
N
N
N
N
Y
Y
Y
Y
Y
Y
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate understanding of GES
N
N
Y
Y
Y
Y
Y
Y
Y
Y
N
N
N
N
N
N
Y
Y
Y
Y
Y
Y
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate capacity
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5f - Description of programme for GES assessment
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats and chapter Bedömning av tillräcklighet
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats and chapter Bedömning av tillräcklighet
a. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - fisk (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats e. See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
a. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet b. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet c. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet d. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats e. See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
Q5g - Gap-filling date for GES assessment
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2020
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q5h - Plans to implement monitoring for GES assessment
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
Q6a -Relevant targets Q6a - Environmental target
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
C.3 C.4
Q6a -Relevant targets Q6a - Associated indicator
Q6b - Adequacy for assessment of targets Q6b_SuitableData
N
N
Y
Y
Y
Y
Y
Y
Y
Y
N
N
N
N
N
N
Y
Y
Y
Y
Y
Y
Y
Y
Q6b - Adequacy for assessment of targets Q6b_EstablishedMethods
N
N
Y
Y
Y
Y
Y
Y
Y
Y
N
N
N
N
N
N
Y
Y
Y
Y
Y
Y
Y
Y
Q6b - Adequacy for assessment of targets Q6d_AdequateCapacity
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6c - Target updating
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6d - Description of programme for targets assessment
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Bedömning av tillräcklighet
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Bedömning av tillräcklighet
See programme Biologisk mångfald - fisk (D1 och 4), chapter Tillräcklighet för bedömning och uppföljning av miljökvalitetsnormer
See programme Biologisk mångfald - fisk (D1 och 4), chapter Tillräcklighet för bedömning och uppföljning av miljökvalitetsnormer
See programme Biologisk mångfald - fisk (D1 och 4), chapter Tillräcklighet för bedömning och uppföljning av miljökvalitetsnormer
See programme Biologisk mångfald - fisk (D1 och 4), chapter Tillräcklighet för bedömning och uppföljning av miljökvalitetsnormer
See programme Biologisk mångfald - fisk (D1 och 4), chapter Tillräcklighet för bedömning och uppföljning av miljökvalitetsnormer
See programme Biologisk mångfald - fisk (D1 och 4), chapter Tillräcklighet för bedömning och uppföljning av miljökvalitetsnormer
See programme Biologisk mångfald - fisk (D1 och 4), chapter Tillräcklighet för bedömning och uppföljning av miljökvalitetsnormer
See programme Biologisk mångfald - fisk (D1 och 4), chapter Tillräcklighet för bedömning och uppföljning av miljökvalitetsnormer
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Bedömning av tillräcklighet
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Bedömning av tillräcklighet, section Miljökvalitetsnormer
Q6e - Gap-filling date for targets assessment
By2020
By2020
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2020
By2020
By2020
By2020
By2020
By2020
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q6f - Plans to implement monitoring for targets assessment
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - fisk (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Slutsatser
Q7a - Relevant activities
  • AgricultForestry
  • CablesPipelines
  • Defence
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • AgricultForestry
  • CablesPipelines
  • Defence
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • CablesPipelines
  • Defence
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • Urban
  • AgricultForestry
  • CablesPipelines
  • Defence
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • Urban
  • AgricultForestry
  • CablesPipelines
  • Defence
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • Urban
  • AgricultForestry
  • CablesPipelines
  • Defence
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • Urban
  • AgricultForestry
  • CablesPipelines
  • Defence
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • Urban
  • AgricultForestry
  • CablesPipelines
  • Defence
  • Dredging
  • Fisheries
  • Industry
  • MiningSandGravel
  • OffshoreStructures
  • OilGas
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
  • AgricultForestry
  • Fisheries
  • Industry
  • Urban
Q7b - Description of monitoring of activities
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - Fåglar (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald - fisk (D1 och 4), chapter Programmets generella ansats
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)
See programme Biologisk mångfald – Marina däggdjur (D1 och 4), chapter Programmets generella ansats, and Slutsatser (Noise)
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
See programme Biologisk mångfald - Kommersiellt nyttjade fiskar och skaldjur (D3), chapter Programmets generella ansats
Q7c - Relevant measures
Q7e - Adequacy for assessment of measures Q7d - Adequate data
Q7e - Adequacy for assessment of measures Q7d - Established methods
Q7e - Adequacy for assessment of measures Q7d - Adequate understanding of GES
Q7e - Adequacy for assessment of measures Q7d - Adequate capacity
Q7e - Adequacy for assessment of measures Q7d - Addresses activities and pressures
Q7e - Adequacy for assessment of measures Q7d - Addresses effectiveness of measures
Q7d - Description of monitoring for measures
Q7f - Gap-filling date for activities and measures
By2020
By2020
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2018
By2018
By2018
By2018
By2018
By2018
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q8a - Links to existing Monitoring Programmes
  • Birds
  • Habitats
  • Other
  • The counts of wintering waterfowl are part of the international waterfowl inventories coordinated internationally by Wetlands International. The program also delivers data for the Eurasian Waterbird Agreement and thus also for the Convention on Wetlands (Ramsaar).
  • Birds
  • Habitats
  • Other
  • The counts of wintering waterfowl are part of the international waterfowl inventories coordinated internationally by Wetlands International. The program also delivers data for the Eurasian Waterbird Agreement and thus also for the Convention on Wetlands (Ramsaar).
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • Habitats
  • OSPAR
  • WFD
  • Habitats
  • OSPAR
  • WFD
  • Habitats
  • OSPAR
  • WFD
  • Habitats
  • OSPAR
  • WFD
  • Habitats
  • OSPAR
  • WFD
  • Habitats
  • OSPAR
  • WFD
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
  • CFP-DC-MAP
  • Habitats
  • OSPAR
Reference sub-programme Sub-programme ID
ANSSE-Birds-D14-Overvintrande
ANSSE-Birds-D14-Overvintrande
ANSSE-COMFISH-D314-Al
ANSSE-COMFISH-D314-Al
ANSSE-Fish-D14-Kust
ANSSE-Fish-D14-Kust
ANSSE-Fish-D14-Tral
ANSSE-Fish-D14-Tral
ANSSE-HAZ-D814-Fiskhalsa
ANSSE-HAZ-D814-Fiskhalsa
ANSSE-HAZ-D814-Salhalsa
ANSSE-HAZ-D814-Salhalsa
ANSSE-mammals-D14-Sal
ANSSE-mammals-D14-Sal
ANSSE-mammals-D14-Tumlare
ANSSE-mammals-D14-Tumlare
ANSSE-COMFISH-D3-Bottenlevande
ANSSE-COMFISH-D3-Bottenlevande
ANSSE-COMFISH-D3-Havskrafta
ANSSE-COMFISH-D3-Havskrafta
ANSSE-COMFISH-D3-Utkast
ANSSE-COMFISH-D3-Utkast
ANSSE-COMFISH-D314-Al
ANSSE-COMFISH-D314-Al
Reference sub-programme Sub-programme name
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - health status
Mobile species - health status
Mobile species - health status
Mobile species - health status
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Q4g - Sub-programmes Sub-programme ID
ANSSE-Birds-D14-Overvintrande
ANSSE-Birds-D14-Overvintrande
ANSSE-COMFISH-D314-Al
ANSSE-COMFISH-D314-Al
ANSSE-Fish-D14-Kust
ANSSE-Fish-D14-Kust
ANSSE-Fish-D14-Tral
ANSSE-Fish-D14-Tral
ANSSE-HAZ-D814-Fiskhalsa
ANSSE-HAZ-D814-Fiskhalsa
ANSSE-HAZ-D814-Salhalsa
ANSSE-HAZ-D814-Salhalsa
ANSSE-mammals-D14-Sal
ANSSE-mammals-D14-Sal
ANSSE-mammals-D14-Tumlare
ANSSE-mammals-D14-Tumlare
ANSSE-COMFISH-D3-Bottenlevande
ANSSE-COMFISH-D3-Bottenlevande
ANSSE-COMFISH-D3-Havskrafta
ANSSE-COMFISH-D3-Havskrafta
ANSSE-COMFISH-D3-Utkast
ANSSE-COMFISH-D3-Utkast
ANSSE-COMFISH-D314-Al
ANSSE-COMFISH-D314-Al
Q4g - Sub-programmes Sub-programme name
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - health status
Mobile species - health status
Mobile species - health status
Mobile species - health status
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental)
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Q4k - Monitoring purpose
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact Pressurse
StateImpact Pressurse
StateImpact
StateImpact
Q4l - Links of monitoring programmes of other Directives and Conventions
"Data from the sub-programme contribute to: Birds Directive Habitats Directive African European Waterfowl Agreement (AEWA) and the Ramsar convention. The monitoring of wintering seabirds are part of the international seabird surveys which are coordinated by Wetlands International.
"Data from the sub-programme contribute to: Birds Directive Habitats Directive African European Waterfowl Agreement (AEWA) and the Ramsar convention. The monitoring of wintering seabirds are part of the international seabird surveys which are coordinated by Wetlands International.
Monitoring is part of the Common Fisheries Policy - Data Collection Framework
Monitoring is part of the Common Fisheries Policy - Data Collection Framework
WFD monitoring Monitoring for the Habitats directive CFP
WFD monitoring Monitoring for the Habitats directive CFP
Monitoring for the Habitats directive CFP HELCOM Monitoring Manual - sub-programme Costal fish (Kattegatt)
Monitoring for the Habitats directive CFP HELCOM Monitoring Manual - sub-programme Costal fish (Kattegatt)
Malformed embryos of eelpout is included in OSPAR pre-CEMP http://www.ospar.org/content/content.asp?menu=00900301400135_000000_000000
Malformed embryos of eelpout is included in OSPAR pre-CEMP http://www.ospar.org/content/content.asp?menu=00900301400135_000000_000000
Sub-programme Health status in HELCOM Monitoring Manual (för Kattegatt)
Sub-programme Health status in HELCOM Monitoring Manual (för Kattegatt)
Habitats Directive OSPAR JAMP
Habitats Directive OSPAR JAMP
Habitats Directive OSPAR JAMP
Habitats Directive OSPAR JAMP
IBTS (The International Bottom Trawl Survey) part of the Common Fisheries Policy - Data Collection Framework OSPAR JAMP - theme B (partly)
IBTS (The International Bottom Trawl Survey) part of the Common Fisheries Policy - Data Collection Framework OSPAR JAMP - theme B (partly)
UWTV part of the Common Fisheries Policy - Data Collection Framework HELCOM Monitoring Manual - sub-programme Commercial shellfish (Kattegatt)
UWTV part of the Common Fisheries Policy - Data Collection Framework HELCOM Monitoring Manual - sub-programme Commercial shellfish (Kattegatt)
Monitoring is part of the Common Fisheries Policy - Data Collection Framework
Monitoring is part of the Common Fisheries Policy - Data Collection Framework
Monitoring is part of the Common Fisheries Policy - Data Collection Framework
Monitoring is part of the Common Fisheries Policy - Data Collection Framework
Q5c - Features Q5c - Habitats
Q5c - Features Q5c - Species list
  • BirdsAll
  • BirdsAll
  • FishCoastal
  • FishDiadromous
  • FishCoastal
  • FishDiadromous
  • FishCoastal
  • FishDiadromous
  • FishCoastal
  • FishDiadromous
  • FishCoastal
  • FishDiadromous
  • FishCoastal
  • FishDiadromous
  • FishCoastal
  • FishDiadromous
  • FishCoastal
  • FishDiadromous
  • MammalsAll
  • MammalsIce
  • MammalsSeals
  • MammalsToothedWhales
  • MammalsAll
  • MammalsIce
  • MammalsSeals
  • MammalsToothedWhales
  • MammalsAll
  • MammalsIce
  • MammalsSeals
  • MammalsToothedWhales
  • MammalsAll
  • MammalsIce
  • MammalsSeals
  • MammalsToothedWhales
  • MammalsAll
  • MammalsIce
  • MammalsSeals
  • MammalsToothedWhales
  • MammalsAll
  • MammalsIce
  • MammalsSeals
  • MammalsToothedWhales
Q5c - Features Q5c - Physical/Chemical features
Q5c - Features Q5c - Pressures
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
  • ExtractSpeciesAll
Q9a - Elements
  • Ducks. F.e. mallard, goldeneye, common eider.Scoters. Common and Velvet scoterGrebes. F.e. Great crested grebe.Swans. Mute and Whooper swan.Divers. F.e. Black-throated diver.Grey heron.Great cormorant.Auks. Common guillemot.
  • Ducks. F.e. mallard, goldeneye, common eider.Scoters. Common and Velvet scoterGrebes. F.e. Great crested grebe.Swans. Mute and Whooper swan.Divers. F.e. Black-throated diver.Grey heron.Great cormorant.Auks. Common guillemot.
  • European eel (Anguilla anguilla)
  • European eel (Anguilla anguilla)
  • All occurring species are noted. Focal species are cod, eelpout and eel
  • All occurring species are noted. Focal species are cod, eelpout and eel
  • All occurring species are noted. Focal species are cod and plaice
  • All occurring species are noted. Focal species are cod and plaice
  • Biological effect monitoring of fish (eelpout)
  • Biological effect monitoring of fish (eelpout)
  • Effects on seal reprodiction.
  • Effects on seal reprodiction.
  • Harbor seal
  • Harbor seal
  • Harbour porpoise
  • Harbour porpoise
  • Herring,Cod, Whiting, Sprat, Eel, Cephalopods (Sepiolidae sp.)
  • Herring,Cod, Whiting, Sprat, Eel, Cephalopods (Sepiolidae sp.)
  • Norwegian lobster (Nephrops norvegicus).
  • Norwegian lobster (Nephrops norvegicus).
  • All species of discarded fish and some crayfish species.
  • All species of discarded fish and some crayfish species.
  • European eel (Anguilla anguilla)
  • European eel (Anguilla anguilla)
Q5a - GES criteria Relevant GES criteria
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 4.3
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 4.3
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 4.2
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 4.2
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 4.2
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 4.2
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 4.2
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 4.2
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 4.2
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 4.2
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 8.2
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 4.3
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 4.3
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 4.3
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 4.3
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 4.3
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 4.3
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 4.3
  • 1.2
  • 1.3
  • 1.6
  • 1.7
  • 3.1
  • 3.2
  • 3.3
  • 4.2
  • 4.3
Q5b - GES indicators Relevant GES indicators
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.3.1
  • 3.3.2
  • 3.3.3
  • 3.3.4
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.3.1
  • 3.3.2
  • 3.3.3
  • 3.3.4
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.3.1
  • 3.3.2
  • 3.3.3
  • 3.3.4
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.3.1
  • 3.3.2
  • 3.3.3
  • 3.3.4
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.3.1
  • 3.3.2
  • 3.3.3
  • 3.3.4
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.3.1
  • 3.3.2
  • 3.3.3
  • 3.3.4
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.3.1
  • 3.3.2
  • 3.3.3
  • 3.3.4
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 1.6.1
  • 1.6.2
  • 1.7.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.3.1
  • 3.3.2
  • 3.3.3
  • 3.3.4
  • 4.2.1
  • 4.3.1
  • GESOther
  • See bilaga 5 Indikatorer
Q9b - Parameters monitored (state/impact) Species distribution
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
Q9b - Parameters monitored (state/impact) Species population size
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
Q9b - Parameters monitored (state/impact) Species population characteristics
  • MP-9b-1-3-1
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-1
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-1
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-3
  • MP-9b-1-3-1
  • MP-9b-1-3-3
Q9b - Parameters monitored (state/impact) Species impacts
  • MP-9b-1-4-1
  • MP-9b-1-4-1
  • MP-9b-1-4-1
  • MP-9b-1-4-1
  • MP-9b-1-4-1
  • MP-9b-1-4-1
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-1
  • MP-9b-1-4-2
  • MP-9b-1-4-1
  • MP-9b-1-4-1
Q9b - Parameters monitored (state/impact) Habitat distribution
Q9b - Parameters monitored (state/impact) Habitat extent
Q9b - Parameters monitored (state/impact) Habitat condition (physical-chemical)
Q9b - Parameters monitored (state/impact) Habitat condition (biological)
  • MP-9b-1-8-2
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-3
  • MP-9b-1-8-3
  • MP-9b-1-8-3
Q9b - Parameters monitored (state/impact) Habitat impacts
  • MP-9b-1-9-1
  • MP-9b-1-9-1
  • MP-9b-1-9-1
  • MP-9b-1-9-1
  • MP-9b-1-9-1
  • MP-9b-1-9-1
  • MP-9b-1-9-1
  • MP-9b-1-9-1
  • MP-9b-1-9-1
  • MP-9b-1-9-1
Q9b - Parameters monitored (pressures) Pressure input
Q9b - Parameters monitored (pressures) Pressure output
Q9b - Parameters monitored (activity) Activity
Q9b Parameters monitored (other) Other
  • MP-9b-4-1-1
  • MP-9b-4-1-1
  • MP-9b-4-1-1
  • MP-9b-4-1-1
Q41 Spatial scope
WFD_CW
WFD_CW
WFD_CW
WFD_CW
WFD_CW
WFD_CW
WFD_CW TerritorialWaters
WFD_CW TerritorialWaters
WFD_CW
WFD_CW
WFD_CW
WFD_CW
WFD_CW
WFD_CW
WFD_CW TerritorialWaters EEZ BeyondMSwaters
WFD_CW TerritorialWaters EEZ BeyondMSwaters
WFD_CW TerritorialWaters EEZ BeyondMSwaters
WFD_CW TerritorialWaters EEZ BeyondMSwaters
TerritorialWaters EEZ BeyondMSwaters
TerritorialWaters EEZ BeyondMSwaters
WFD_CW TerritorialWaters EEZ BeyondMSwaters
WFD_CW TerritorialWaters EEZ BeyondMSwaters
WFD_CW
WFD_CW
Q4j - Description of spatial scope
See sub-programme Övervintrande sjöfågel, chapter Rumslig och tidsmässig täckning
See sub-programme Övervintrande sjöfågel, chapter Rumslig och tidsmässig täckning
See sub-programme Migrerande fiskarter - ål, chapter Rumslig och tidsmässig täckning
See sub-programme Migrerande fiskarter - ål, chapter Rumslig och tidsmässig täckning
See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning
See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning
See sub-programme Kustprovtrålning, chapter Rumslig och tidsmässig omfattning
See sub-programme Kustprovtrålning, chapter Rumslig och tidsmässig omfattning
See sub-programme Hälsotillstånd hos kustfisk, chapter Rumslig och tidsmässig täckning
See sub-programme Hälsotillstånd hos kustfisk, chapter Rumslig och tidsmässig täckning
See sub-programme Hälsotillstånd hos säl, chapter Rumslig och tidsmässig täckning
See sub-programme Hälsotillstånd hos säl, chapter Rumslig och tidsmässig täckning
See sub-programme Bestånd av säl, chapter Rumslig och tidsmässig täckning
See sub-programme Bestånd av säl, chapter Rumslig och tidsmässig täckning
See sub-programme Bestånd av tumlare, chapter Rumslig och tidsmässig täckning
See sub-programme Bestånd av tumlare, chapter Rumslig och tidsmässig täckning
See sub-programme Bottenlevande fisk, chapter Rumslig och tidsmässig täckning
See sub-programme Bottenlevande fisk, chapter Rumslig och tidsmässig täckning
See sub-programme Havskräfta, chapter Rumslig och tidsmässig täckning
See sub-programme Havskräfta, chapter Rumslig och tidsmässig täckning
See sub-programme Utkast av fisk, chapter Rumslig och tidsmässig täckning
See sub-programme Utkast av fisk, chapter Rumslig och tidsmässig täckning
See sub-programme Migrerande fiskarter - ål, chapter Rumslig och tidsmässig täckning
See sub-programme Migrerande fiskarter - ål, chapter Rumslig och tidsmässig täckning
Marine Unit IDs
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
  • ANS-SE-SR-Nordsjon
Q4h - Temporal scope Start date- End date
1967-9999
1967-9999
2004-9999
2004-9999
1969-9999
1969-9999
2001-9999
2001-9999
1989-9999
1989-9999
2009-9999
2009-9999
1988-9999
1988-9999
1994-9999
1994-9999
1972-9999
1972-9999
2011-9999
2011-9999
1996-9999
1996-9999
2004-9999
2004-9999
Q9h - Temporal resolution of sampling
  • Yearly
  • Yearly
  • Yearly
  • Yearly
  • Yearly
  • Yearly
  • Yearly
  • Yearly
  • Yearly
  • Yearly
  • Frequency depends on found and reported dead seals, as well as hunted seals. Hence it varies.
  • Other
  • Frequency depends on found and reported dead seals, as well as hunted seals. Hence it varies.
  • Other
  • Yearly
  • Yearly
  • Irregularly (1994, 2005, 2013, 2016)
  • Other
  • Irregularly (1994, 2005, 2013, 2016)
  • Other
  • 6monthly
  • 6monthly
  • Yearly
  • Yearly
  • 3monthly
  • 3monthly
  • Yearly
  • Yearly
Q9c - Monitoring method
Standardized censuses of wintering birds, in accordance with IWC methods. Censuses of birds - individual counts of staging and wintering seabirds - BIN 16.1 and BIN 16.3, Naturvårdsverket 1978 http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/BIN_F_16_sjofagel.pdf
Standardized censuses of wintering birds, in accordance with IWC methods. Censuses of birds - individual counts of staging and wintering seabirds - BIN 16.1 and BIN 16.3, Naturvårdsverket 1978 http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/BIN_F_16_sjofagel.pdf
Test fishing is carried out according to methods under revison and descriptions of methods will be avalible on the web in the future.
Test fishing is carried out according to methods under revison and descriptions of methods will be avalible on the web in the future.
Test fishing with fyke nets according to the Swedish monitoring method described in "Provfiske med kustöversikttsnät, nätlänkar och ryssjor". (will be updated during 2014) https://www.havochvatten.se/download/18.64f5b3211343cffddb2800029/Provfiske+med+kust%C3%B6versiktsn%C3%A4t,+n%C3%A4tl%C3%A4nkar+och+ryssjor+p%C3%A5+kustn%C3%A4ra+grunt+vatten.pdf
Test fishing with fyke nets according to the Swedish monitoring method described in "Provfiske med kustöversikttsnät, nätlänkar och ryssjor". (will be updated during 2014) https://www.havochvatten.se/download/18.64f5b3211343cffddb2800029/Provfiske+med+kust%C3%B6versiktsn%C3%A4t,+n%C3%A4tl%C3%A4nkar+och+ryssjor+p%C3%A5+kustn%C3%A4ra+grunt+vatten.pdf
Test fishing with trawl carried out according to method which is under revision and according to manuals for international coordinated surveys (ICES 2010, ICES 2012a, ICES 2014).
Test fishing with trawl carried out according to method which is under revision and according to manuals for international coordinated surveys (ICES 2010, ICES 2012a, ICES 2014).
Undersökningstyp Hälsotillstånd hos kustfisk – biologiska effekter på subcellulär och cellulär nivå http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/Undersokningstyper/kust%20och%20hav/fiskhalso.pdf
Undersökningstyp Hälsotillstånd hos kustfisk – biologiska effekter på subcellulär och cellulär nivå http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/Undersokningstyper/kust%20och%20hav/fiskhalso.pdf
Undersökningstyp Patologi hos gråsäl, vikaresäl och knubbsäl http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/Undersokningstyper/kust%20och%20hav/salpatologi.pdf
Undersökningstyp Patologi hos gråsäl, vikaresäl och knubbsäl http://www.naturvardsverket.se/upload/stod-i-miljoarbetet/vagledning/miljoovervakning/Handledning/Metoder/Undersokningstyper/kust%20och%20hav/salpatologi.pdf
Bestånd av knubbsäl och vikaresäl https://www.havochvatten.se/download/18.64f5b3211343cffddb280003193/1348912813047/Metodbeskrivning+Best%C3%A5nd+av+knubbs%C3%A4l+och+vikares%C3%A4l.pdf
Bestånd av knubbsäl och vikaresäl https://www.havochvatten.se/download/18.64f5b3211343cffddb280003193/1348912813047/Metodbeskrivning+Best%C3%A5nd+av+knubbs%C3%A4l+och+vikares%C3%A4l.pdf
The SCANS surveys; aerial and/or ship based line transect surveys. Hammond PS et al., 2002. Abundance of harbour porpoise and other cetaceans in the North Sea and adjacent waters. Journal of Applied Ecology, 39, 361–376. (SCANS) Hammond PS et al., 2013. Cetacean abundance and distribution in European Atlantic shelf waters to inform conservation and management. Biological Conservation, 164, 107–122. (SCANS-II)
The SCANS surveys; aerial and/or ship based line transect surveys. Hammond PS et al., 2002. Abundance of harbour porpoise and other cetaceans in the North Sea and adjacent waters. Journal of Applied Ecology, 39, 361–376. (SCANS) Hammond PS et al., 2013. Cetacean abundance and distribution in European Atlantic shelf waters to inform conservation and management. Biological Conservation, 164, 107–122. (SCANS-II)
ICES 2010. Manual for the International Bottom Trawl Surveys. ADDENDUM 1: IBTS MANUAL - REVISION VIII. The International Bottom Trawl Survey Working Group, Copenhagen 2010. 73 s http://www.slu.se/Documents/externwebben/akvatiska-resurser/personliga%20sidor/2010%20IBTS%20Manual_Rev_VIII.pdf
ICES 2010. Manual for the International Bottom Trawl Surveys. ADDENDUM 1: IBTS MANUAL - REVISION VIII. The International Bottom Trawl Survey Working Group, Copenhagen 2010. 73 s http://www.slu.se/Documents/externwebben/akvatiska-resurser/personliga%20sidor/2010%20IBTS%20Manual_Rev_VIII.pdf
Workshop on the Use of UWTV Surveys for Determining Abundance in Nephrops Stocks throughout European Waters. 17–21 April 2007, Heraklion, Crete, Greece. ICES CM 2007/ACFM:14.
Workshop on the Use of UWTV Surveys for Determining Abundance in Nephrops Stocks throughout European Waters. 17–21 April 2007, Heraklion, Crete, Greece. ICES CM 2007/ACFM:14.
Sampling according to methods suggested by ICES expert groups (e.g. WKPRECISE, WKMERGE, SGPIDS and WKPICS)
Sampling according to methods suggested by ICES expert groups (e.g. WKPRECISE, WKMERGE, SGPIDS and WKPICS)
Test fishing is carried out according to methods under revison and descriptions of methods will be avalible on the web in the future.
Test fishing is carried out according to methods under revison and descriptions of methods will be avalible on the web in the future.
Q9d - Description of alteration to method
See sub-programme Bottenlevande fisk, chapter Metoder
See sub-programme Bottenlevande fisk, chapter Metoder
See sub-programme Havskräfta, chapter Metoder
See sub-programme Havskräfta, chapter Metoder
Q9e - Quality assurance
  • Unknown
  • Unknown
  • Data quality assured internally when storing in the national database (KUL) through embedded and subjective plausibility checks.
  • National
  • Data quality assured internally when storing in the national database (KUL) through embedded and subjective plausibility checks.
  • National
  • Other
  • The data host SLU are developing a system för QA/QC during 2014
  • Other
  • The data host SLU are developing a system för QA/QC during 2014
  • Unknown
  • Unknown
  • National
  • Nationell standard (Naturvårdsverkets kvalitetssystem för samordnad miljöövervakning)
  • National
  • Nationell standard (Naturvårdsverkets kvalitetssystem för samordnad miljöövervakning)
  • National
  • Nationell standard (Naturvårdsverkets kvalitetssystem för samordnad miljöövervakning)
  • National
  • Nationell standard (Naturvårdsverkets kvalitetssystem för samordnad miljöövervakning)
  • Other
  • Power and sensitivity analyses coordinated through HELCOM seal group. Methodology coordinated between Sweden, Denmark and Norway.
  • Other
  • Power and sensitivity analyses coordinated through HELCOM seal group. Methodology coordinated between Sweden, Denmark and Norway.
  • Unknown
  • Unknown
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • Other
  • Reference footage
  • ICESDataTypeGuide
  • Other
  • Reference footage
  • ICESDataTypeGuide
  • ICESDataTypeGuide
  • Data quality assured internally when storing in the national database (KUL) through embedded and subjective plausibility checks.
  • National
  • Data quality assured internally when storing in the national database (KUL) through embedded and subjective plausibility checks.
  • National
Q9f - Quality control
OtherQC
OtherQC
DelayedValidation
DelayedValidation
OtherQC
OtherQC
RealandDelayedValidation
RealandDelayedValidation
Unknown
Unknown
Unknown
Unknown
RealValidation
RealValidation
RealValidation
RealValidation
RealandDelayedValidation
RealandDelayedValidation
OtherQC
OtherQC
RealandDelayedValidation
RealandDelayedValidation
DelayedValidation
DelayedValidation
Q9g - Spatial resolution of sampling Q9g - Proportion of area covered %
40
40
40
40
43
43
100
100
10
10
100
100
100
100
100
100
100
100
35
35
40
40
Q9g - Spatial resolution of sampling Q9g - No. of samples
Approximately 150 counting units annually. In addition, country wide survey are carried out at irregular intervals, the last in 2004
Approximately 150 counting units annually. In addition, country wide survey are carried out at irregular intervals, the last in 2004
1 sample from 4 locations = 4 samples/year
1 sample from 4 locations = 4 samples/year
1 sample from 5 locations = 5 samples/year
1 sample from 5 locations = 5 samples/year
36 prover per år i området
36 prover per år i området
25 samples from 1 location = 25 samples/year
25 samples from 1 location = 25 samples/year
Geographic scope depends on found and reported dead seals, as well as hunted seals. Hence it varies. Seals found dead each day, all year, and hunted harbour seals collected during hunting (May and August-December). Number varies
Geographic scope depends on found and reported dead seals, as well as hunted seals. Hence it varies. Seals found dead each day, all year, and hunted harbour seals collected during hunting (May and August-December). Number varies
3 counts per year during the moult
3 counts per year during the moult
Line transect survey based on equal probability sampling. No info on the actual coverage
Line transect survey based on equal probability sampling. No info on the actual coverage
146 samples/year
146 samples/year
1 sample from 90 locations = 90 samples/year
1 sample from 90 locations = 90 samples/year
76 fishing trips = 76 samples/year
76 fishing trips = 76 samples/year
1 sample from 4 locations = 4 samples/year
1 sample from 4 locations = 4 samples/year
Q9i - Description of sample representivity
See sub-programme Övervintrande sjöfågel, chapter Rumslig och tidsmässig täckning
See sub-programme Övervintrande sjöfågel, chapter Rumslig och tidsmässig täckning
See sub-programme Migrerande fisk - ål, parameter table and chapter Rumslig och tidsmässig täckning
See sub-programme Migrerande fisk - ål, parameter table and chapter Rumslig och tidsmässig täckning
See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning
See sub-programme Kustprovfiske, chapter Rumslig och tidsmässig omfattning
See sub-programme Kustprovtrålning, chapter Rumslig och tidsmässig omfattning See sub-programme Kustprovtrålning, chapter Metoder
See sub-programme Kustprovtrålning, chapter Rumslig och tidsmässig omfattning See sub-programme Kustprovtrålning, chapter Metoder
See sub-programme Hälsotillstånd hos kustfisk, chapter Rumslig och tidsmässig täckning
See sub-programme Hälsotillstånd hos kustfisk, chapter Rumslig och tidsmässig täckning
During hunting season: May and August-December
During hunting season: May and August-December
See sub-programme Bestånd av säl, chapter Rumslig och tidsmässig täckning and Metoder (QA/QC) See sub-programme Bestånd av säl, parameter table
See sub-programme Bestånd av säl, chapter Rumslig och tidsmässig täckning and Metoder (QA/QC) See sub-programme Bestånd av säl, parameter table
See sub-programme Bestånd av tumlare, chapter Rumslig och tidsmässig täckning See sub-programme Bestånd av tumlare, parameter table.
See sub-programme Bestånd av tumlare, chapter Rumslig och tidsmässig täckning See sub-programme Bestånd av tumlare, parameter table.
See sub-programme Bottenlevande fisk, parameter table and chapter Rumslig och tidsmässig täckning
See sub-programme Bottenlevande fisk, parameter table and chapter Rumslig och tidsmässig täckning
See sub-programme Havskräfta, chapter Rumslig och tidsmässig täckning
See sub-programme Havskräfta, chapter Rumslig och tidsmässig täckning
See sub-programme Utkast av fisk, parameter table and chapter Rumslig och tidsmässig täckning
See sub-programme Utkast av fisk, parameter table and chapter Rumslig och tidsmässig täckning
See sub-programme Migrerande fisk - ål, parameter table and chapter Rumslig och tidsmässig täckning
See sub-programme Migrerande fisk - ål, parameter table and chapter Rumslig och tidsmässig täckning
Q10a - Scale for aggregation of data
  • Other
  • See 10b
  • Other
  • See 10b
  • Subregion
  • Subregion
  • Unknown
  • Unknown
  • Region
  • Region
  • Other
  • See 10b
  • Other
  • See 10b
  • Other
  • See 10b
  • Other
  • See 10b
  • Subregion
  • Subregion
  • Subregion
  • Subregion
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
  • Subregion
  • Subregion
Q10b - Other scale for aggregation of data
Other: Since the surveys are part of an international project, Swedish data can be aggregated with the other participating countries' data at different geographical levels.
Other: Since the surveys are part of an international project, Swedish data can be aggregated with the other participating countries' data at different geographical levels.
See sub-programme Hälsotillstånd hos kustfisk, chapter Metoder
See sub-programme Hälsotillstånd hos kustfisk, chapter Metoder
Se sub-programme Hälsotillstånd hos säl, chapter Metoder
Se sub-programme Hälsotillstånd hos säl, chapter Metoder
Q10c - Access to monitoring data Q10c - Data type
UnprocessedData ProcessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData ProcessedData DataProducts
UnprocessedData DataProducts
UnprocessedData DataProducts
UnprocessedData DataProducts Simulated
UnprocessedData DataProducts Simulated
UnprocessedData
UnprocessedData
UnprocessedData
UnprocessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
UnprocessedData ProcessedData
Q10c - Access to monitoring data Q10c - Data access mechanism
LocationInternationalDC
LocationInternationalDC
LocationNationalDC
LocationNationalDC
URLdownload
URLdownload
URLdownload
URLdownload
URLdownload
URLdownload
URLdownload
URLdownload
URLdownload
URLdownload
LocationNationalDC
LocationNationalDC
URLdownload
URLdownload
LocationNationalDC
LocationNationalDC
LocationInternationalDC
LocationInternationalDC
LocationNationalDC
LocationNationalDC
Q10c - Access to monitoring data Q10c - Data access rights
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
RestrictedSpecific
RestrictedSpecific
Open
Open
Q10c - Access to monitoring data Q10c - INSPIRE standard
Q10c - Access to monitoring data Q10c Date data are available
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
2014-09
Q10c - Access to monitoring data Q10c - Data update frequency
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Other
Other
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Q10d - Description of data access
See sub-programme Övervintrande sjöfågel, chapter Var finns data
See sub-programme Övervintrande sjöfågel, chapter Var finns data
See sub-programme Migrerande fiskarter - ål, chapter Var finns data
See sub-programme Migrerande fiskarter - ål, chapter Var finns data
See sub-programme Kustprovfiske, chapter Var finns data
See sub-programme Kustprovfiske, chapter Var finns data
See sub-programme Kustprovtrålning, chapter Var finns data
See sub-programme Kustprovtrålning, chapter Var finns data
See sub-programme Hälsotillstånd hos kustfisk, chapter Var finns data
See sub-programme Hälsotillstånd hos kustfisk, chapter Var finns data
Se sub-programme Hälsotillstånd hos säl, chapter Var finns data
Se sub-programme Hälsotillstånd hos säl, chapter Var finns data
See sub-programme Bestånd av säl, chapter Var finns data
See sub-programme Bestånd av säl, chapter Var finns data
See sub-programme Bestånd av tumlare, chapter Var finns data
See sub-programme Bestånd av tumlare, chapter Var finns data
See sub-programme Bottenlevande fisk, parameter table and chapter Var finns data
See sub-programme Bottenlevande fisk, parameter table and chapter Var finns data
See sub-programme Havskräfta, chapter Var finns data
See sub-programme Havskräfta, chapter Var finns data
See sub-programme Utkast av fisk, chapter Var finns data
See sub-programme Utkast av fisk, chapter Var finns data
See sub-programme Migrerande fiskarter - ål, chapter Var finns data
See sub-programme Migrerande fiskarter - ål, chapter Var finns data
Descriptor
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
D1.4
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D1.4
Monitoring strategy description
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
The monitoring of fish provides a basis for assessing state based on the size of the stocks, size distribution, spawning biomass and health conditions for certain species. These parameters can be affected by a variety of human activities. Fish stocks are directly affected by fishing activities and variation in environmental variables such as salinity, temperature and oxygen conditions. Fish stocks can also be affected by changes in the food web, as a result of, for example, overfishing, climate change, alien species, hunting of seals and seabirds and eutrophication, as well as by the exploitation of spawning and nursery areas. In addition, hazardous substances can lead to damage and diseases in the fish community. The monitoring of by-catch, recreational fishing and commercial fishing provides a basis for direct impact. At the same time, other human activities and pressures that may affect fish, such as physical disturbance and inputs of pollutants, are included in other monitoring strategies. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries.
Coverage of GES criteria
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Gaps and plans
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Monitoring enable assessment of all primary criterias, however the spatial resolution should be improved in some basins. By using data on activities and pressures the aim is to combine these data together with data on fish to be able to assess D1C5. Coastal fish – Gaps for D1C2 were identified in the IA 2018 in some basins, but have since been improved. A revision of the programme has been carried out to improve data used for status assessment. More data on certain species like pike, vendace and grayling are needed to improve the confidence. Offshore fish - BITS and IBTS are being developed within ICES, especially to provide data on fish on an ecosystem level. In the monitoring of commercial fisheries there´s a common aim to intensify and deepen the cooperation between countries using regional plans. Methods are developed in ICES WGCATCH, and coordination of data management in RCG Baltic, RCG North Sea and Eastern Arctic. Migratory fish – The number of salmon monitoring locations is evaluated continously due to habitat restorations and removing migration barriers. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate. Health status - After reports of sick fish with leisures in Hanöbukten the Swedish gouvernment appointed SwAM to investigate this further and to find the causes. Monitoring of flounder started in 2016 and was later included in the programme. To add more wild fish species, crayfish and molluscs new monitoring started in 2020. Recreational fishing – A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. Bycatch – Monitoring is being improved thanks to a number of ongoing projects. These are complementing the regular monitoring of commersial fisheries discards, where human observers are used, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Related targets
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • ANSSE-C.3_Population_fisk_ålder_storlek_bestånd
  • ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek
  • BALSE-C.3_Population_fisk_ålder_storlek_bestånd
  • BALSE-C.4_Samhälle_fisk_förkomst_art_storlek
Coverage of targets
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Related measures
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
  • ANSSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • ANSSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • ANSSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M039 - 'Common Fisheries Policy'
  • BALSE-M004 - 'ÅPH 4 – New fishing regulations to protect particularly threatened stocks that spawn in coastal waters'
  • BALSE-M005 - 'ÅPH 5 – New fishing regulations to promote more selective fishing in coastal waters'
  • BALSE-M006 - 'ÅPH 6 – Fishing regulations to reduce fishing pressure on coastal stocks'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M024 - 'ÅPH 24 - developing a comprehensive framework for national action programmes for threatened species and habitats in the marine environment, and coordinating such efforts nationally'
  • BALSE-M039 - 'Common Fisheries Policy'
Coverage of measures
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Related monitoring programmes
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
  • SE-D1D2D7-outfalls
  • SE-D1D3-bycatch
  • SE-D1D3-comfishing
  • SE-D1D3-eel
  • SE-D1D3-recreationalfishing
  • SE-D1D3-salmon
  • SE-D1D3D4-coastalfish
  • SE-D1D3D4-offshorefish
  • SE-D1D8-fishhealth
Programme code
SE-D1D2D7-outfalls
SE-D1D2D7-outfalls
SE-D1D2D7-outfalls
SE-D1D2D7-outfalls
SE-D1D2D7-outfalls
SE-D1D2D7-outfalls
SE-D1D2D7-outfalls
SE-D1D2D7-outfalls
SE-D1D2D7-outfalls
SE-D1D3-bycatch
SE-D1D3-bycatch
SE-D1D3-comfishing
SE-D1D3-comfishing
SE-D1D3-eel
SE-D1D3-eel
SE-D1D3-recreationalfishing
SE-D1D3-recreationalfishing
SE-D1D3-salmon
SE-D1D3-salmon
SE-D1D3D4-coastalfish
SE-D1D3D4-coastalfish
SE-D1D3D4-coastalfish
SE-D1D3D4-coastalfish
SE-D1D3D4-coastalfish
SE-D1D3D4-coastalfish
SE-D1D3D4-coastalfish
SE-D1D3D4-coastalfish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D3D4-offshorefish
SE-D1D8-fishhealth
SE-D1D8-fishhealth
SE-D1D8-fishhealth
SE-D1D8-fishhealth
Programme name
Effects of outfalls from power stations
Effects of outfalls from power stations
Effects of outfalls from power stations
Effects of outfalls from power stations
Effects of outfalls from power stations
Effects of outfalls from power stations
Effects of outfalls from power stations
Effects of outfalls from power stations
Effects of outfalls from power stations
Bycatch
Bycatch
Commercial fisheries
Commercial fisheries
Migratory fish (eel)
Migratory fish (eel)
Recreational fisheries
Recreational fisheries
Migratory fish (salmon)
Migratory fish (salmon)
Coastal fish
Coastal fish
Coastal fish
Coastal fish
Coastal fish
Coastal fish
Coastal fish
Coastal fish
Offshore fish
Offshore fish
Offshore fish
Offshore fish
Offshore fish
Offshore fish
Offshore fish
Offshore fish
Offshore fish
Offshore fish
Offshore fish
Offshore fish
Fish health status
Fish health status
Fish health status
Fish health status
Update type
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
New programme
New programme
Modified from 2014
Modified from 2014
New programme
New programme
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Old programme codes
  • ANSSE-HYDRO-D72-Kylvatten
  • BALSE-HYDRO-D72-Kylvatten
  • ANSSE-HYDRO-D72-Kylvatten
  • BALSE-HYDRO-D72-Kylvatten
  • ANSSE-HYDRO-D72-Kylvatten
  • BALSE-HYDRO-D72-Kylvatten
  • ANSSE-HYDRO-D72-Kylvatten
  • BALSE-HYDRO-D72-Kylvatten
  • ANSSE-HYDRO-D72-Kylvatten
  • BALSE-HYDRO-D72-Kylvatten
  • ANSSE-HYDRO-D72-Kylvatten
  • BALSE-HYDRO-D72-Kylvatten
  • ANSSE-HYDRO-D72-Kylvatten
  • BALSE-HYDRO-D72-Kylvatten
  • ANSSE-HYDRO-D72-Kylvatten
  • BALSE-HYDRO-D72-Kylvatten
  • ANSSE-HYDRO-D72-Kylvatten
  • BALSE-HYDRO-D72-Kylvatten
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D314-Al
  • BALSE-COMFISH-D314-Al
  • ANSSE-COMFISH-D314-Al
  • BALSE-COMFISH-D314-Al
  • BALSE-COMFISH-D314-Lax
  • BALSE-COMFISH-D314-Lax
  • ANSSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Tral
  • BALSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Tral
  • BALSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Tral
  • BALSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Tral
  • BALSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Tral
  • BALSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Tral
  • BALSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Tral
  • BALSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Kust
  • ANSSE-Fish-D14-Tral
  • BALSE-Fish-D14-Kust
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Bottenlevande
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Bottenlevande
  • BALSE-COMFISH-D3-Pelagisk
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-HAZ-D814-Fiskhalsa
  • BALSE-HAZ-D814-Fiskhalsa
  • ANSSE-HAZ-D814-Fiskhalsa
  • BALSE-HAZ-D814-Fiskhalsa
  • ANSSE-HAZ-D814-Fiskhalsa
  • BALSE-HAZ-D814-Fiskhalsa
  • ANSSE-HAZ-D814-Fiskhalsa
  • BALSE-HAZ-D814-Fiskhalsa
Programme description
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas. To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005. Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below. The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased.
In the regular sampling carried out on board commercial fishing vessels in accordance with EU data collection regulations ((EU) 2017/1004, (EU) 2016/1251), as well as the regulation on the conservation of fishery resources and the protection of marine ecosystems (EU ) 2019/1241, information regarding by-catch is obtained. All fish species, commercial shellfish, mammals and birds are noted. Sampling takes place mainly on vessels fishing with various bottom trawls. Data collection carried out according to the EU data collection regulations is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES´s various expert groups (for by-catches mainly WGBYC). Sweden participates actively in these groups. Pilot studies were carried out in 2017-2019 with the aim of conducting by-catch sampling in 2020 in fisheries that use passive gear (nets and hooks). The purpose is to increase knowledge about by-catches in these fisheries, to test whether it is possible to estimate by-catches by having observers on board fishing boats, and if this is an effective method. Sampling of nets in the Sound and in the Kattegat will be included in the regular sampling from 2020. However, no ongoing monitoring of passive gear is currently planned in the Baltic Proper as previous pilots observed fewer by-catches there. So based on risk, monitoring in the Sound and Kattegatt are therefore prioritized. The Skagerrak could possibly be added after the pilot study there is completed in 2021. The pilot studies have shown that it also works to monitor the fish with passive gear with the help of observers (the challenge is that the vessels are small). However, the question remains whether this is the most effective way of estimating the total amount of by-catches in the fisheries. The problem is that observers can only cover a small part of the total fishing effort and that by-catches of many species (such as harbour porpoises and various birds) are relatively uncommon. This means that there will be few observations and thus uncertainty in the estimates of the total amount of by-catches. In 2020, therefore, a new pilot project was initiated where surveillance with the help of cameras is tested and compared with surveillance with the help
In the regular sampling carried out on board commercial fishing vessels in accordance with EU data collection regulations ((EU) 2017/1004, (EU) 2016/1251), as well as the regulation on the conservation of fishery resources and the protection of marine ecosystems (EU ) 2019/1241, information regarding by-catch is obtained. All fish species, commercial shellfish, mammals and birds are noted. Sampling takes place mainly on vessels fishing with various bottom trawls. Data collection carried out according to the EU data collection regulations is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES´s various expert groups (for by-catches mainly WGBYC). Sweden participates actively in these groups. Pilot studies were carried out in 2017-2019 with the aim of conducting by-catch sampling in 2020 in fisheries that use passive gear (nets and hooks). The purpose is to increase knowledge about by-catches in these fisheries, to test whether it is possible to estimate by-catches by having observers on board fishing boats, and if this is an effective method. Sampling of nets in the Sound and in the Kattegat will be included in the regular sampling from 2020. However, no ongoing monitoring of passive gear is currently planned in the Baltic Proper as previous pilots observed fewer by-catches there. So based on risk, monitoring in the Sound and Kattegatt are therefore prioritized. The Skagerrak could possibly be added after the pilot study there is completed in 2021. The pilot studies have shown that it also works to monitor the fish with passive gear with the help of observers (the challenge is that the vessels are small). However, the question remains whether this is the most effective way of estimating the total amount of by-catches in the fisheries. The problem is that observers can only cover a small part of the total fishing effort and that by-catches of many species (such as harbour porpoises and various birds) are relatively uncommon. This means that there will be few observations and thus uncertainty in the estimates of the total amount of by-catches. In 2020, therefore, a new pilot project was initiated where surveillance with the help of cameras is tested and compared with surveillance with the help
Commercial fishing in this case refers to the commercial fishing that requires a fishing license and has an obligation to report its fishing activity. The obligation to report their catches and fishing activities is governed by both EU legislation and Swedish legislation. This information is used for the national quota allocation for fish stocks and as a basis for the biological stock estimate (see also programmes Offshore fish and coastal fish). Economic statistics are collected to monitor economic drivers in the fisheries sector. The statistics are collected to meet the requirements from the EU via Regulation (EU) 2017/1004 and implementing decisions (EU) 2019/909 and (EU) 2019/910. In addition to this reporting, statistics are used within the Swedish Fisheries Administration. In addition to the pressure in the form of extracting fish, the monitoring of other parts of the fishing activities' impact is described in the programmes Physical disturbance and loss (bottom trawling) and in By-catch.
Commercial fishing in this case refers to the commercial fishing that requires a fishing license and has an obligation to report its fishing activity. The obligation to report their catches and fishing activities is governed by both EU legislation and Swedish legislation. This information is used for the national quota allocation for fish stocks and as a basis for the biological stock estimate (see also programmes Offshore fish and coastal fish). Economic statistics are collected to monitor economic drivers in the fisheries sector. The statistics are collected to meet the requirements from the EU via Regulation (EU) 2017/1004 and implementing decisions (EU) 2019/909 and (EU) 2019/910. In addition to this reporting, statistics are used within the Swedish Fisheries Administration. In addition to the pressure in the form of extracting fish, the monitoring of other parts of the fishing activities' impact is described in the programmes Physical disturbance and loss (bottom trawling) and in By-catch.
Eels are monitored along the West Coast and the Baltic Sea. Eels along the Swedish coast are found in three life stages, which are glass eels, yellow eels and silver eels. The monitoring aims to provide a knowledge base for the management of eels. On the West Coast, eels are monitored through fisheries-independent sampling because eel fishing on the West Coast, north of Torekov, is not permitted. In the Baltic Sea, eels are monitored by sampling in commercial fishing. Most studies regarding migratory young eels are done in traps that catch very small yellow eels on migration in running water, in two studies migratory silver eels are caught. The programme describes the composition with respect to age and size at all stages of life. In addition, marking/tagging is done with the aim of estimating the proportion that is caught in commercial fishing, at the same time as an estimate is made of the size of the coastal stock. This monitoring programme applies to eels in the sea. Eels are also caught in freshwater to monitor the impact of, among other things, fishing and hydropower. This monitoring is not described here. Sweden's monitoring is coordinated with other countries that carry out monitoring of eels, by Sweden reporting every three years to ICES, who compiles an overview based on the countries' reporting to an overview analysis that covers the entire eel range (Europe, North Africa and West Asia). Monitoring data from Sweden and other countries are used here, to examine weighted trends in the occurrence of eels, the nature of eels, threats to eels and recommendations for a better knowledge base. Ices also issues annual scientific advice on the eel. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate.
Eels are monitored along the West Coast and the Baltic Sea. Eels along the Swedish coast are found in three life stages, which are glass eels, yellow eels and silver eels. The monitoring aims to provide a knowledge base for the management of eels. On the West Coast, eels are monitored through fisheries-independent sampling because eel fishing on the West Coast, north of Torekov, is not permitted. In the Baltic Sea, eels are monitored by sampling in commercial fishing. Most studies regarding migratory young eels are done in traps that catch very small yellow eels on migration in running water, in two studies migratory silver eels are caught. The programme describes the composition with respect to age and size at all stages of life. In addition, marking/tagging is done with the aim of estimating the proportion that is caught in commercial fishing, at the same time as an estimate is made of the size of the coastal stock. This monitoring programme applies to eels in the sea. Eels are also caught in freshwater to monitor the impact of, among other things, fishing and hydropower. This monitoring is not described here. Sweden's monitoring is coordinated with other countries that carry out monitoring of eels, by Sweden reporting every three years to ICES, who compiles an overview based on the countries' reporting to an overview analysis that covers the entire eel range (Europe, North Africa and West Asia). Monitoring data from Sweden and other countries are used here, to examine weighted trends in the occurrence of eels, the nature of eels, threats to eels and recommendations for a better knowledge base. Ices also issues annual scientific advice on the eel. Eel is partly monitored using data from commercial fisheries, but since no new licencies are approved this data flow will eventually stop and need to be replaced with monitoring. We are collaborating with DK to tag eels in the Baltic sea and monitor them in the Sound and Danish straits to learn where eels migrate.
Recreational fishing in Sweden is defined as all fishing that does not take place with the support of a commercial fishing license. Recreational fishing includes both fishing with hand gear (eg rod) and catching gear (eg nets). Recreational fishing in Sweden is extensive and therefore good knowledge is needed about the practitioners, where to fish and what is caught. As part of the work to understand and describe the scope and impact, statistics on recreational fishing have been collected since the 1970s to form the basis for decisions within the administration. The first survey was part of the 1973 fishing water investigation, which was also followed up during the 1990s. In 2011, the SwAM became the coordinating agency for official statistics in the area of fishing and was thus given the responsibility to annually collect statistics regarding the extent of recreational fishing in Sweden. This collection takes place via a national survey that started in 2013 and is progressing in roughly the same direction and design today. In addition to the national survey, several fishing sites are visited on a regular basis since 2012. Data collection is carried out annually in the Sound and the southern Baltic Sea in accordance with EU regulations ((EU) 2019/909 and (EU) 2019/910). The data collection aims to cover the fishing for cod and by-catches in this fishery (see programme Bycatch). Monitoring frequency is three times per year (4-monthly). A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. An ongoing project initiated by Sportfiskarna is about developing an application – FångstDatabanken (Citizen science) for catch reporting. SwAM has since the start in 2012 been part of their reference and development group. Data collection carried out under the EU Data Collection Regulation is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups, RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES 'various expert groups (for recreational fishing, especially WGRFS). Sweden participates actively in these g
Recreational fishing in Sweden is defined as all fishing that does not take place with the support of a commercial fishing license. Recreational fishing includes both fishing with hand gear (eg rod) and catching gear (eg nets). Recreational fishing in Sweden is extensive and therefore good knowledge is needed about the practitioners, where to fish and what is caught. As part of the work to understand and describe the scope and impact, statistics on recreational fishing have been collected since the 1970s to form the basis for decisions within the administration. The first survey was part of the 1973 fishing water investigation, which was also followed up during the 1990s. In 2011, the SwAM became the coordinating agency for official statistics in the area of fishing and was thus given the responsibility to annually collect statistics regarding the extent of recreational fishing in Sweden. This collection takes place via a national survey that started in 2013 and is progressing in roughly the same direction and design today. In addition to the national survey, several fishing sites are visited on a regular basis since 2012. Data collection is carried out annually in the Sound and the southern Baltic Sea in accordance with EU regulations ((EU) 2019/909 and (EU) 2019/910). The data collection aims to cover the fishing for cod and by-catches in this fishery (see programme Bycatch). Monitoring frequency is three times per year (4-monthly). A pilot study (2017-2019) found that the main part of cod catches in southern Baltic Sea and the Sound comes from recreational fishing in the Sound. The monitoring will therefore focus on this during 2020-2021. SwAM is also collaborating with SLU to develop a longterm plan for monitoring of recreational fishing. An ongoing project initiated by Sportfiskarna is about developing an application – FångstDatabanken (Citizen science) for catch reporting. SwAM has since the start in 2012 been part of their reference and development group. Data collection carried out under the EU Data Collection Regulation is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups, RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES 'various expert groups (for recreational fishing, especially WGRFS). Sweden participates actively in these g
The monitoring includes the collection of biological data for wild salmon stocks (salmon rivers) as well as statistics for releases and fishing for both wild and farmed salmon. The purpose of the monitoring is to monitor the status and development of wild salmon stocks and to investigate the effects of fishing and hydropower. The purpose of the biological advice is to contribute to the overall goals for salmon management being met both nationally and internationally. These goals are to protect and rebuild weak wild salmon stocks so that they can gradually reach the management goal of Maximum Sustainable Yield (MSY). Sweden's monitoring is coordinated with similar work in other countries, through guidelines and agreements developed within ICES, the North Atlantic Salmon Conservation Organization (NASCO), the Regional Coordination Groups (EU RCG) and HELCOM. Sweden actively participates in the regional coordination.
The monitoring includes the collection of biological data for wild salmon stocks (salmon rivers) as well as statistics for releases and fishing for both wild and farmed salmon. The purpose of the monitoring is to monitor the status and development of wild salmon stocks and to investigate the effects of fishing and hydropower. The purpose of the biological advice is to contribute to the overall goals for salmon management being met both nationally and internationally. These goals are to protect and rebuild weak wild salmon stocks so that they can gradually reach the management goal of Maximum Sustainable Yield (MSY). Sweden's monitoring is coordinated with similar work in other countries, through guidelines and agreements developed within ICES, the North Atlantic Salmon Conservation Organization (NASCO), the Regional Coordination Groups (EU RCG) and HELCOM. Sweden actively participates in the regional coordination.
Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish
Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish
Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish
Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish
Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish
Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish
Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish
Coastal fish refer to the fish species that live a significant part of their lives in the coastal ecosystem, such as flounder (Platichthys flesus), perch (Perca fluviatilis) and eelpout (Zoarces viviparus). Coastal fish monitoring (trawls, nets, hydroacoustics) aims to describe changes in the fishing community as a whole, in terms of species composition, relative occurrence of different species and size structure. In addition, changes at species level are followed up by analyzing changes in the number and size structure of the most common species in the catch. In some surveys, individual sampling of selected species is performed. The individual sampling aims to provide information about, for example, individual weight and condition, and provides material for further analysis of, for example, age and fish health. The state of coastal fish reflects the coastal ecosystem and the impact of small-scale coastal fishing and recreational fishing (see programmes Commercial fisheries and Recreational fisheries). Long-term changes in the abundance of different functional groups of coastal fish can also be affected by eutrophication, deteriorating habitats and changes in predation. The latter may be due to imbalance in the food web due to human impact such as fishing and loss of important habitats. Monitoring in the Baltic Sea started in 1960 while in the North Sea it started in 1969. Abramis bjoerkna, Arnoglossus laterna, Callionymus lyra, Chelidonichthys gurnardus, Myoxocephalus scorpius and Trachinus draco are also monitored but they were not included in the element lists for Coastal fish nor Commercial fish
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.
Monitoring, where biological effects are studied at both subcellular and cellular levels, can be used to describe the general state of health of different organisms and provides an opportunity to demonstrate the toxicity of unknown and known substances in a study area. The national monitoring of the health status of coastal fish aims to use proven and sensitive methods to demonstrate the presence and effects in fish of a possible large-scale impact of hazardous substances in coastal reference areas in the Baltic Sea and the North Sea. The aim of the monitoring is to be able to describe the current state of the environment in coastal reference areas regarding effects of mainly hazardous substances on the state of fish health by following time trends of biochemical, physiological, histological and pathological effect variables in fish. The surveys shall also provide reference data for surveys on fish in regionally and locally affected areas and provide a basis for monitoring environmental quality objectives, regional environmental objectives and the effects of measures taken to reduce chemical emissions. The national monitoring of fish health began with surveys of perch in 1988 in the Baltic Sea and in 1989 the programme was expanded with eelpout from the North Sea. During 2020-2021, the monitoring of the effects of hazardous substances will be evaluated in order to be able to optimize the monitoring programmes both in terms of coverage and costs and to provide a better basis for state assessment and determining the causes of the effects.
Monitoring, where biological effects are studied at both subcellular and cellular levels, can be used to describe the general state of health of different organisms and provides an opportunity to demonstrate the toxicity of unknown and known substances in a study area. The national monitoring of the health status of coastal fish aims to use proven and sensitive methods to demonstrate the presence and effects in fish of a possible large-scale impact of hazardous substances in coastal reference areas in the Baltic Sea and the North Sea. The aim of the monitoring is to be able to describe the current state of the environment in coastal reference areas regarding effects of mainly hazardous substances on the state of fish health by following time trends of biochemical, physiological, histological and pathological effect variables in fish. The surveys shall also provide reference data for surveys on fish in regionally and locally affected areas and provide a basis for monitoring environmental quality objectives, regional environmental objectives and the effects of measures taken to reduce chemical emissions. The national monitoring of fish health began with surveys of perch in 1988 in the Baltic Sea and in 1989 the programme was expanded with eelpout from the North Sea. During 2020-2021, the monitoring of the effects of hazardous substances will be evaluated in order to be able to optimize the monitoring programmes both in terms of coverage and costs and to provide a better basis for state assessment and determining the causes of the effects.
Monitoring, where biological effects are studied at both subcellular and cellular levels, can be used to describe the general state of health of different organisms and provides an opportunity to demonstrate the toxicity of unknown and known substances in a study area. The national monitoring of the health status of coastal fish aims to use proven and sensitive methods to demonstrate the presence and effects in fish of a possible large-scale impact of hazardous substances in coastal reference areas in the Baltic Sea and the North Sea. The aim of the monitoring is to be able to describe the current state of the environment in coastal reference areas regarding effects of mainly hazardous substances on the state of fish health by following time trends of biochemical, physiological, histological and pathological effect variables in fish. The surveys shall also provide reference data for surveys on fish in regionally and locally affected areas and provide a basis for monitoring environmental quality objectives, regional environmental objectives and the effects of measures taken to reduce chemical emissions. The national monitoring of fish health began with surveys of perch in 1988 in the Baltic Sea and in 1989 the programme was expanded with eelpout from the North Sea. During 2020-2021, the monitoring of the effects of hazardous substances will be evaluated in order to be able to optimize the monitoring programmes both in terms of coverage and costs and to provide a better basis for state assessment and determining the causes of the effects.
Monitoring, where biological effects are studied at both subcellular and cellular levels, can be used to describe the general state of health of different organisms and provides an opportunity to demonstrate the toxicity of unknown and known substances in a study area. The national monitoring of the health status of coastal fish aims to use proven and sensitive methods to demonstrate the presence and effects in fish of a possible large-scale impact of hazardous substances in coastal reference areas in the Baltic Sea and the North Sea. The aim of the monitoring is to be able to describe the current state of the environment in coastal reference areas regarding effects of mainly hazardous substances on the state of fish health by following time trends of biochemical, physiological, histological and pathological effect variables in fish. The surveys shall also provide reference data for surveys on fish in regionally and locally affected areas and provide a basis for monitoring environmental quality objectives, regional environmental objectives and the effects of measures taken to reduce chemical emissions. The national monitoring of fish health began with surveys of perch in 1988 in the Baltic Sea and in 1989 the programme was expanded with eelpout from the North Sea. During 2020-2021, the monitoring of the effects of hazardous substances will be evaluated in order to be able to optimize the monitoring programmes both in terms of coverage and costs and to provide a better basis for state assessment and determining the causes of the effects.
Monitoring purpose
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Environmental state and impacts
  • Environmental state and impacts
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
Other policies and conventions
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
Regional cooperation - coordinating body
  • Other
  • Other
  • Other
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • Other
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
Regional cooperation - countries involved
DE,DK,FI
DE,DK,FI
Regional cooperation - implementation level
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Joint data collection
Joint data collection
Joint data collection
Joint data collection
Joint data collection
Joint data collection
Joint data collection
Joint data collection
Joint data collection
Joint data collection
Joint data collection
Joint data collection
Monitoring details
Features
Non-renewable energy generation
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Coastal fish
Demersal shelf fish
Pelagic shelf fish
Newly introduced non-indigenous species
Established non-indigenous species
Hydrographical changes
Input of other forms of energy (including electromagnetic fields, light and heat)
Fish and shellfish harvesting (professional, recreational)
Species affected by incidental by-catch
Fish and shellfish harvesting (professional, recreational)
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Coastal fish
Coastal fish
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Fish and shellfish harvesting (professional, recreational)
Pelagic shelf fish
Pelagic shelf fish
Coastal fish
Coastal fish
Coastal fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Coastal ecosystems
Coastal ecosystems
Demersal shelf fish
Pelagic shelf fish
Demersal shelf fish
Pelagic shelf fish
Demersal shelf fish
Pelagic shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Shelf ecosystems
Shelf ecosystems
Shelf ecosystems
Coastal fish
Demersal shelf fish
Coastal ecosystems
Adverse effects on species or habitats
Non-renewable energy generation
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Coastal fish
Demersal shelf fish
Pelagic shelf fish
Newly introduced non-indigenous species
Established non-indigenous species
Hydrographical changes
Input of other forms of energy (including electromagnetic fields, light and heat)
Fish and shellfish harvesting (professional, recreational)
Species affected by incidental by-catch
Fish and shellfish harvesting (professional, recreational)
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Coastal fish
Coastal fish
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Fish and shellfish harvesting (professional, recreational)
Pelagic shelf fish
Pelagic shelf fish
Coastal fish
Coastal fish
Coastal fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Coastal ecosystems
Coastal ecosystems
Demersal shelf fish
Pelagic shelf fish
Demersal shelf fish
Pelagic shelf fish
Demersal shelf fish
Pelagic shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Shelf ecosystems
Shelf ecosystems
Shelf ecosystems
Coastal fish
Demersal shelf fish
Coastal ecosystems
Adverse effects on species or habitats
Non-renewable energy generation
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Coastal fish
Demersal shelf fish
Pelagic shelf fish
Newly introduced non-indigenous species
Established non-indigenous species
Hydrographical changes
Input of other forms of energy (including electromagnetic fields, light and heat)
Fish and shellfish harvesting (professional, recreational)
Species affected by incidental by-catch
Fish and shellfish harvesting (professional, recreational)
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Coastal fish
Coastal fish
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Fish and shellfish harvesting (professional, recreational)
Pelagic shelf fish
Pelagic shelf fish
Coastal fish
Coastal fish
Coastal fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Coastal ecosystems
Coastal ecosystems
Demersal shelf fish
Pelagic shelf fish
Demersal shelf fish
Pelagic shelf fish
Demersal shelf fish
Pelagic shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Shelf ecosystems
Shelf ecosystems
Shelf ecosystems
Coastal fish
Demersal shelf fish
Coastal ecosystems
Adverse effects on species or habitats
Non-renewable energy generation
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Coastal fish
Demersal shelf fish
Pelagic shelf fish
Newly introduced non-indigenous species
Established non-indigenous species
Hydrographical changes
Input of other forms of energy (including electromagnetic fields, light and heat)
Fish and shellfish harvesting (professional, recreational)
Species affected by incidental by-catch
Fish and shellfish harvesting (professional, recreational)
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Coastal fish
Coastal fish
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Fish and shellfish harvesting (professional, recreational)
Pelagic shelf fish
Pelagic shelf fish
Coastal fish
Coastal fish
Coastal fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Coastal ecosystems
Coastal ecosystems
Demersal shelf fish
Pelagic shelf fish
Demersal shelf fish
Pelagic shelf fish
Demersal shelf fish
Pelagic shelf fish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Shelf ecosystems
Shelf ecosystems
Shelf ecosystems
Coastal fish
Demersal shelf fish
Coastal ecosystems
Adverse effects on species or habitats
Elements
  • Abramis brama
  • Alburnus alburnus
  • Anguilla anguilla
  • Blicca bjoerkna
  • Ciliata mustela
  • Ctenolabrus rupestris
  • Esox lucius
  • Gadus morhua
  • Gasterosteus aculeatus
  • Gobius niger
  • Gymnocephalus cernua
  • Labrus bergylta
  • Leuciscus idus
  • Neogobius melanostomus
  • Platichthys flesus
  • Rutilus rutilus
  • Sander lucioperca
  • Scardinius erythrophthalmus
  • Symphodus melops
  • Syngnathus acus
  • Tinca tinca
  • Zoarces viviparus
  • Myoxocephalus scorpius
  • Perca fluviatilis
  • Pleuronectes platessa
  • Syngnathus typhle
  • Taurulus bubalis
  • Clupea harengus
  • Not Applicable
  • Alkmaria romijni
  • Bonnemaisonia hamifera
  • Crassostrea gigas
  • Dasya baillouviana
  • Hemigrapsus sanguineus
  • Marenzelleria spp. (neglecta & viridis)
  • Neogobius melanostomus
  • Oncorhynchus mykiss
  • Potamopyrgus antipodarum
  • Sargassum muticum
  • Spermothamnion repens var. flagelliferum
  • Temperature
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Anguilla anguilla
  • Anguilla anguilla
  • Not Applicable
  • Not Applicable
  • Salmo salar
  • Salmo trutta trutta
  • Salmo salar
  • Salmo trutta trutta
  • Alburnus alburnus
  • Coregonus maraena
  • Ctenolabrus rupestris
  • Gadus morhua
  • Gobius niger
  • Gymnocephalus cernua
  • Osmerus eperlanus
  • Platichthys flesus
  • Rutilus rutilus
  • Sander lucioperca
  • Scardinius erythrophthalmus
  • Symphodus melops
  • Zoarces viviparus
  • Alburnus alburnus
  • Coregonus maraena
  • Ctenolabrus rupestris
  • Gadus morhua
  • Gobius niger
  • Gymnocephalus cernua
  • Osmerus eperlanus
  • Platichthys flesus
  • Rutilus rutilus
  • Sander lucioperca
  • Scardinius erythrophthalmus
  • Symphodus melops
  • Zoarces viviparus
  • Alburnus alburnus
  • Coregonus maraena
  • Ctenolabrus rupestris
  • Gadus morhua
  • Gobius niger
  • Gymnocephalus cernua
  • Osmerus eperlanus
  • Platichthys flesus
  • Rutilus rutilus
  • Sander lucioperca
  • Scardinius erythrophthalmus
  • Symphodus melops
  • Zoarces viviparus
  • Anguilla anguilla
  • Clupea harengus
  • Ctenolabrus rupestris
  • Gadus morhua
  • Limanda limanda
  • Melanogrammus aeglefinus
  • Merlangius merlangus
  • Perca fluviatilis
  • Platichthys flesus
  • Pleuronectes platessa
  • Pollachius virens
  • Rutilus rutilus
  • Sander lucioperca
  • Scophthalmus rhombus
  • Solea solea
  • Symphodus melops
  • Anguilla anguilla
  • Clupea harengus
  • Ctenolabrus rupestris
  • Gadus morhua
  • Limanda limanda
  • Melanogrammus aeglefinus
  • Merlangius merlangus
  • Perca fluviatilis
  • Platichthys flesus
  • Pleuronectes platessa
  • Pollachius virens
  • Rutilus rutilus
  • Sander lucioperca
  • Scophthalmus rhombus
  • Solea solea
  • Symphodus melops
  • Fish community
  • Fish community
  • Fish community
  • Amblyraja radiata
  • Anguilla anguilla
  • Argentina silus
  • Coryphaenoides rupestris
  • Dicentrarchus labrax
  • Eutrigla gurnardus
  • Gadus morhua
  • Glyptocephalus cynoglossus
  • Limanda limanda
  • Lophius piscatorius
  • Melanogrammus aeglefinus
  • Merlangius merlangus
  • Merluccius merluccius
  • Micromesistius poutassou
  • Microstomus kitt
  • Molva molva
  • Phycis blennoides
  • Platichthys flesus
  • Pleuronectes platessa
  • Pollachius pollachius
  • Pollachius virens
  • Raja clavata
  • Scophthalmus maximus
  • Scophthalmus rhombus
  • Scyliorhinus canicula
  • Solea solea (sin. vulgaris)
  • Trachurus trachurus
  • Clupea harengus
  • Cyclopterus lumpus
  • Dicentrarchus labrax
  • Scomber scombrus
  • Sprattus sprattus
  • Squalus acanthias
  • Amblyraja radiata
  • Anguilla anguilla
  • Argentina silus
  • Coryphaenoides rupestris
  • Dicentrarchus labrax
  • Eutrigla gurnardus
  • Gadus morhua
  • Glyptocephalus cynoglossus
  • Limanda limanda
  • Lophius piscatorius
  • Melanogrammus aeglefinus
  • Merlangius merlangus
  • Merluccius merluccius
  • Micromesistius poutassou
  • Microstomus kitt
  • Molva molva
  • Phycis blennoides
  • Platichthys flesus
  • Pleuronectes platessa
  • Pollachius pollachius
  • Pollachius virens
  • Raja clavata
  • Scophthalmus maximus
  • Scophthalmus rhombus
  • Scyliorhinus canicula
  • Solea solea (sin. vulgaris)
  • Trachurus trachurus
  • Clupea harengus
  • Cyclopterus lumpus
  • Dicentrarchus labrax
  • Scomber scombrus
  • Sprattus sprattus
  • Squalus acanthias
  • Amblyraja radiata
  • Anguilla anguilla
  • Argentina silus
  • Coryphaenoides rupestris
  • Dicentrarchus labrax
  • Eutrigla gurnardus
  • Gadus morhua
  • Glyptocephalus cynoglossus
  • Limanda limanda
  • Lophius piscatorius
  • Melanogrammus aeglefinus
  • Merlangius merlangus
  • Merluccius merluccius
  • Micromesistius poutassou
  • Microstomus kitt
  • Molva molva
  • Phycis blennoides
  • Platichthys flesus
  • Pleuronectes platessa
  • Pollachius pollachius
  • Pollachius virens
  • Raja clavata
  • Scophthalmus maximus
  • Scophthalmus rhombus
  • Scyliorhinus canicula
  • Solea solea (sin. vulgaris)
  • Trachurus trachurus
  • Clupea harengus
  • Cyclopterus lumpus
  • Dicentrarchus labrax
  • Scomber scombrus
  • Sprattus sprattus
  • Squalus acanthias
  • Amblyraja radiata
  • Ammodytes spp.
  • Anguilla anguilla
  • Argentina silus
  • Cancer pagurus
  • Clupea harengus
  • Coryphaenoides rupestris
  • Dicentrarchus labrax
  • Eutrigla gurnardus
  • Gadus morhua
  • Glyptocephalus cynoglossus
  • Limanda limanda
  • Lophius piscatorius
  • Melanogrammus aeglefinus
  • Merlangius merlangus
  • Merluccius merluccius
  • Micromesistius poutassou
  • Microstomus kitt
  • Molva molva
  • Nephrops norvegicus
  • Pandalus borealis
  • Phycis blennoides
  • Platichthys flesus
  • Pleuronectes platessa
  • Pollachius pollachius
  • Pollachius virens
  • Raja clavata
  • Scomber scombrus
  • Scophthalmus maximus
  • Scophthalmus rhombus
  • Scyliorhinus canicula
  • Solea solea
  • Sprattus sprattus
  • Squalus acanthias
  • Trachurus trachurus
  • Trisopterus esmarkii
  • Amblyraja radiata
  • Ammodytes spp.
  • Anguilla anguilla
  • Argentina silus
  • Cancer pagurus
  • Clupea harengus
  • Coryphaenoides rupestris
  • Dicentrarchus labrax
  • Eutrigla gurnardus
  • Gadus morhua
  • Glyptocephalus cynoglossus
  • Limanda limanda
  • Lophius piscatorius
  • Melanogrammus aeglefinus
  • Merlangius merlangus
  • Merluccius merluccius
  • Micromesistius poutassou
  • Microstomus kitt
  • Molva molva
  • Nephrops norvegicus
  • Pandalus borealis
  • Phycis blennoides
  • Platichthys flesus
  • Pleuronectes platessa
  • Pollachius pollachius
  • Pollachius virens
  • Raja clavata
  • Scomber scombrus
  • Scophthalmus maximus
  • Scophthalmus rhombus
  • Scyliorhinus canicula
  • Solea solea
  • Sprattus sprattus
  • Squalus acanthias
  • Trachurus trachurus
  • Trisopterus esmarkii
  • Amblyraja radiata
  • Ammodytes spp.
  • Anguilla anguilla
  • Argentina silus
  • Cancer pagurus
  • Clupea harengus
  • Coryphaenoides rupestris
  • Dicentrarchus labrax
  • Eutrigla gurnardus
  • Gadus morhua
  • Glyptocephalus cynoglossus
  • Limanda limanda
  • Lophius piscatorius
  • Melanogrammus aeglefinus
  • Merlangius merlangus
  • Merluccius merluccius
  • Micromesistius poutassou
  • Microstomus kitt
  • Molva molva
  • Nephrops norvegicus
  • Pandalus borealis
  • Phycis blennoides
  • Platichthys flesus
  • Pleuronectes platessa
  • Pollachius pollachius
  • Pollachius virens
  • Raja clavata
  • Scomber scombrus
  • Scophthalmus maximus
  • Scophthalmus rhombus
  • Scyliorhinus canicula
  • Solea solea
  • Sprattus sprattus
  • Squalus acanthias
  • Trachurus trachurus
  • Trisopterus esmarkii
  • Fish community
  • Fish community
  • Fish community
  • Zoarces viviparus
  • Perca fluviatilis
  • Fish community
  • Perca fluviatilis
  • Zoarces viviparus
GES criteria
D1C2
D1C2
D1C2
D2C1
D2C2
D7C1
D7C1
D1C1
D3C1
D1C2
D1C4
D3C1
NotRelevan
D1C2
D1C4
D1C2
D1C3
D1C4
D3C2
D3C3
D4C1
D4C2
D4C3
D1C2
D1C2
D1C3
D1C3
D1C4
D1C4
D3C1
D3C2
D3C3
D4C1
D4C2
D4C3
D1C3
D1C3
D4C4
D8C2
Parameters
  • Abundance (number of individuals)
  • Biomass
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Abundance (number of individuals)
  • Biomass
  • Presence
  • Abundance (number of individuals)
  • Biomass
  • Extent
  • Other
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Abundance (number of individuals)
  • Biomass
  • Other
  • Distribution (range)
  • Mortality (weight/volume; number of individuals)
  • Other
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Other
  • Distribution (range)
  • Abundance (number of individuals)
  • Biomass
  • Age distribution
  • Other
  • Sex distribution
  • Distribution (range)
  • Distribution (spatial)
  • Abundance (number of individuals)
  • Biomass of Spawning Stock (SSB)
  • Length
  • Other
  • Size distribution
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Size distribution
  • Abundance (number of individuals)
  • Biomass
  • Abundance (number of individuals)
  • Biomass
  • Age distribution
  • Length
  • Other
  • Sex distribution
  • Age distribution
  • Length
  • Other
  • Sex distribution
  • Distribution (range)
  • Distribution (range)
  • Mortality (weight/volume; number of individuals)
  • Abundance (number of individuals)
  • Biomass of Spawning Stock (SSB)
  • Length
  • Size distribution
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Size distribution
  • Age distribution
  • Length
  • Other
  • Age distribution
  • Length
  • Other
  • Other
  • Other
Parameter Other
Size distribution
temperature
Length Mass Age distribution Lifestage Stage of ma
Species composition, Size distribution, and Inform
Information regarding the fisherman, fishing metho
Age distribution Lifestage Presence of parasites (
Developmental state of gonads Presence of parasite
Mass
Species composition
Mass Size distribution Developmental state of gona
Mass Size distribution Developmental state of gona
Species composition
Mass
Mass
Age distribution Mass Length
Visual inspection of external and internal defects
Spatial scope
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
Marine reporting units
  • ANS-SE-AA-B_Kattegatt
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-BG_Vasterhavet
  • BAL-SE-AA-BG_Bottniska_Viken
  • BAL-SE-AA-BG_Egentliga_Ostersjon
  • ANS-SE-AA-BG_Vasterhavet
  • BAL-SE-AA-BG_Bottniska_Viken
  • BAL-SE-AA-BG_Egentliga_Ostersjon
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_V_Gotlandshavet
Temporal scope (start date - end date)
1968-9999
1968-9999
1968-9999
1968-9999
1968-9999
1968-9999
1968-9999
1968-9999
1968-9999
1996-9999
1996-9999
1994-9999
1994-9999
1969-9999
1969-9999
1973-9999
1973-9999
2004-9999
2004-9999
1960-9999
1960-9999
1960-9999
1960-9999
1960-9999
1960-9999
1960-9999
1960-9999
1972-9999
1972-9999
1972-9999
1972-9999
1972-9999
1972-9999
1972-9999
1972-9999
1972-9999
1972-9999
1972-9999
1972-9999
1988-9999
1988-9999
1988-9999
1988-9999
Monitoring frequency
Other
Other
Other
Other
Other
Other
Other
Other
Other
3-monthly
3-monthly
Continually
Continually
Yearly
Yearly
Other
Other
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Yearly
Yearly
Yearly
Yearly
Monitoring type
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • Other
  • Visual observation
  • Other
  • Visual observation
  • Administrative data collection
  • Other
  • Administrative data collection
  • Other
  • In-situ sampling coastal
  • In-situ sampling coastal
  • Administrative data collection
  • In-situ sampling coastal
  • Visual observation
  • Administrative data collection
  • In-situ sampling coastal
  • Visual observation
  • Administrative data collection
  • In-situ sampling coastal
  • Remote surveillance
  • Administrative data collection
  • In-situ sampling coastal
  • Remote surveillance
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
Monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • NEAFC: Recording of Catch and Fishing Effort
  • Other monitoring method
  • NEAFC: Recording of Catch and Fishing Effort
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • HELCOM Guidelines for coastal fish monitoring
  • Other monitoring method
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • OSPAR JAMP Guidelines for Contaminant-Specific Biological Effects (Agreement 2008-09) (Replaces Agreement 2003-10)
  • OSPAR JAMP Guidelines for General Biological Effects Monitoring. Revised technical annexes 2007 (Agreement 2007-07)
  • Other monitoring method
  • OSPAR JAMP Guidelines for Contaminant-Specific Biological Effects (Agreement 2008-09) (Replaces Agreement 2003-10)
  • OSPAR JAMP Guidelines for General Biological Effects Monitoring. Revised technical annexes 2007 (Agreement 2007-07)
  • Other monitoring method
  • OSPAR JAMP Guidelines for Contaminant-Specific Biological Effects (Agreement 2008-09) (Replaces Agreement 2003-10)
  • OSPAR JAMP Guidelines for General Biological Effects Monitoring. Revised technical annexes 2007 (Agreement 2007-07)
  • Other monitoring method
  • OSPAR JAMP Guidelines for Contaminant-Specific Biological Effects (Agreement 2008-09) (Replaces Agreement 2003-10)
  • OSPAR JAMP Guidelines for General Biological Effects Monitoring. Revised technical annexes 2007 (Agreement 2007-07)
  • Other monitoring method
Monitoring method other
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/ https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html"
Catches and by-catches are monitored with the help of observers who accompany the fishing vessels during commercial fishing. The regular sampling is divided into area, fisheries and quarters. This means that observations are made every quarter from different types of bottom trawls (shrimp trawl, crayfish trawl with grate, trawl without grate). Usually, in the order of 0.5-2% (different for different types of fisheries) of commercial fishing trips are observed. The fishing trips observed are selected at random. Observations of by-catch within the framework of the pilot studies are carried out in the same manner. The observers examine the entire process during which the fishing gear is hauled so that also by-catches that do not follow on board but fall out of the nets can be registered. Furthermore, the observers examine the entire sorting of the catch. The observers then measure and weigh the catch and take samples for biological analysis. Remote surveillance using cameras onboard is being tested during 2020, and may supplement the monitoring in the future.
Catches and by-catches are monitored with the help of observers who accompany the fishing vessels during commercial fishing. The regular sampling is divided into area, fisheries and quarters. This means that observations are made every quarter from different types of bottom trawls (shrimp trawl, crayfish trawl with grate, trawl without grate). Usually, in the order of 0.5-2% (different for different types of fisheries) of commercial fishing trips are observed. The fishing trips observed are selected at random. Observations of by-catch within the framework of the pilot studies are carried out in the same manner. The observers examine the entire process during which the fishing gear is hauled so that also by-catches that do not follow on board but fall out of the nets can be registered. Furthermore, the observers examine the entire sorting of the catch. The observers then measure and weigh the catch and take samples for biological analysis. Remote surveillance using cameras onboard is being tested during 2020, and may supplement the monitoring in the future.
"https://www.havochvatten.se/fiske-och-handel/rapportering-och-e-tjanster/yrkesfiske/manualer-for-verksamma-inom-yrkesfisket.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/lagstiftning-direktiv-och-forordningar/lagstiftning-som-ror-yrkesfisket.html "
"https://www.havochvatten.se/fiske-och-handel/rapportering-och-e-tjanster/yrkesfiske/manualer-for-verksamma-inom-yrkesfisket.html https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/lagstiftning-direktiv-och-forordningar/lagstiftning-som-ror-yrkesfisket.html "
Several different methods are used in eel monitoring. In the North Sea, test fishing with eel traps place, similar to the method described in the method standard ”Provfiske med kustöversiktsnät, nätlänkar och ryssjor” on coastal shallow water. In the Baltic Sea, eels are collected through commercial fishing within the framework of DCF. Sampling with stationary trawl takes place in the intake channel of cooling water to Ringhals nuclear power plant and catches glass eels. The method is described in the reports from the Biological recipient control at Ringhals nuclear power plant. By tagging and then recapturing the tagged eel on the Baltic coast, a measure is obtained of how hard the fishing pressure is (ICES report WGEEL 2018).
Several different methods are used in eel monitoring. In the North Sea, test fishing with eel traps place, similar to the method described in the method standard ”Provfiske med kustöversiktsnät, nätlänkar och ryssjor” on coastal shallow water. In the Baltic Sea, eels are collected through commercial fishing within the framework of DCF. Sampling with stationary trawl takes place in the intake channel of cooling water to Ringhals nuclear power plant and catches glass eels. The method is described in the reports from the Biological recipient control at Ringhals nuclear power plant. By tagging and then recapturing the tagged eel on the Baltic coast, a measure is obtained of how hard the fishing pressure is (ICES report WGEEL 2018).
There is currently no method that captures all data in a cost-effective way. Therefore, it is important to choose the right method(s) to answer the questions asked. Data of interest may be of a biological or non-biological nature. Biological data include, for example, the number and sizes of fish caught. Non-biological data can be, for example, different measures of effort, characterization of practitioners and socio-economic aspects. The methods are described separately below, but a preferred data collection is in most cases a combination of the methods to provide a comprehensive knowledge base of the structure of the fishery, participants and their activity and catches, including re-released catches. Depending on which question or questions are to be answered, methods can be combined flexibly. National survey The survey uses a panel design with a stratified random sample. More information regarding the design of the survey is summarized in a quality declaration - https://www.havochvatten.se/download/18.619e9cdf163fb20d0dd815a1/1529477995525/kvalitetsdeklaration-2017.pdf . Site visiting studies Site-visiting studies include, for example, inventories and interviews of recreational fishermen in port or during fishing. Inventories can be made by boat, in port or by plane. The pilot study in the Sound and the Southern Baltic Sea includes several different fishing methods. Therefore, the methodology differs depending on which fishing method is studied. Sampling takes place at random at all landing sites in the area (tour boats, charter boats, private boats and fishing from land) to describe the extent of recreational fishing, the number of fishermen and the amount of fish. More about this project is described here: https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/fritidsfiske/. More information about recreational fishing surveys, its methods and the overall work in Sweden can be read in SLU Aqua's Aqua reports - https://www.slu.se/globalassets/ew/org/inst/aqua/externwebb/sidan-publikationer/aqua-reports-xxxx_xx/aquarapporter/2018/aqua-reports-2018_22.pdf.
There is currently no method that captures all data in a cost-effective way. Therefore, it is important to choose the right method(s) to answer the questions asked. Data of interest may be of a biological or non-biological nature. Biological data include, for example, the number and sizes of fish caught. Non-biological data can be, for example, different measures of effort, characterization of practitioners and socio-economic aspects. The methods are described separately below, but a preferred data collection is in most cases a combination of the methods to provide a comprehensive knowledge base of the structure of the fishery, participants and their activity and catches, including re-released catches. Depending on which question or questions are to be answered, methods can be combined flexibly. National survey The survey uses a panel design with a stratified random sample. More information regarding the design of the survey is summarized in a quality declaration - https://www.havochvatten.se/download/18.619e9cdf163fb20d0dd815a1/1529477995525/kvalitetsdeklaration-2017.pdf . Site visiting studies Site-visiting studies include, for example, inventories and interviews of recreational fishermen in port or during fishing. Inventories can be made by boat, in port or by plane. The pilot study in the Sound and the Southern Baltic Sea includes several different fishing methods. Therefore, the methodology differs depending on which fishing method is studied. Sampling takes place at random at all landing sites in the area (tour boats, charter boats, private boats and fishing from land) to describe the extent of recreational fishing, the number of fishermen and the amount of fish. More about this project is described here: https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/fritidsfiske/. More information about recreational fishing surveys, its methods and the overall work in Sweden can be read in SLU Aqua's Aqua reports - https://www.slu.se/globalassets/ew/org/inst/aqua/externwebb/sidan-publikationer/aqua-reports-xxxx_xx/aquarapporter/2018/aqua-reports-2018_22.pdf.
https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/fisk-i-rinnande-vatten---vadningselfiske.html
https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/fisk-i-rinnande-vatten---vadningselfiske.html
"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."
"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."
"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."
"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."
"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."
"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."
"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."
"https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html Monitoring of vendace, which resides in the free water column are done with special sonar (vendace survey). These register the amount of fish on a predetermined distance. Trawl hauls are carried out at regular intervals to estimate the size composition. In addition to this, vendace is also sampled through on-board and harbor sampling in commercial fishing. This sampling is described in more detail in programmes Offshore fish and By-catch (for non-target species)."
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html
https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/halsotillstand-hos-kustfisk.html
https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/halsotillstand-hos-kustfisk.html
https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/halsotillstand-hos-kustfisk.html
https://www.havochvatten.se/hav/vagledning--lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/halsotillstand-hos-kustfisk.html
Quality control
https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
Sampling takes place through a random selection of ships/voyages. The observers bring with them a manual for determining the species of birds and also photograph captured birds as much as possible. Data is registered in the national database Fiskdata2 according to the updated manual. Data is examined and checked in several respects. Quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers).
Sampling takes place through a random selection of ships/voyages. The observers bring with them a manual for determining the species of birds and also photograph captured birds as much as possible. Data is registered in the national database Fiskdata2 according to the updated manual. Data is examined and checked in several respects. Quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers).
Commercial fishing reporting is standardized. The information is validated and checked during physical and administrative control by SwAM and the Coast Guard. Physical inspections are carried out on site on the ships in port by SwAM and at sea by the Swedish Coast Guard. Quality assurance of the economic statistics is carried out according to proven methods and practices.
Commercial fishing reporting is standardized. The information is validated and checked during physical and administrative control by SwAM and the Coast Guard. Physical inspections are carried out on site on the ships in port by SwAM and at sea by the Swedish Coast Guard. Quality assurance of the economic statistics is carried out according to proven methods and practices.
The quality assurance is conducted by strictly following standardized methodology. Quality assurance takes place within the data hosting at SLU. Data is quality assured electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material.
The quality assurance is conducted by strictly following standardized methodology. Quality assurance takes place within the data hosting at SLU. Data is quality assured electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material.
QC of the national survey is summarized in a quality declaration - https://www.havochvatten.se/download/18.619e9cdf163fb20d0dd815a1/1529477995525/kvalitetsdeklaration-2017.pdf . QC of the Site visiting studies is described in the final reports of each projects - https://www.slu.se/globalassets/ew/org/inst/aqua/externwebb/sidan-publikationer/aqua-reports-xxxx_xx/aquarapporter/2018/aqua-reports-2018_22.pdf. The methods carried out on the basis of EU data collection regulations, including the pilot projects, are also evaluated by ICES working group WGRFS.
QC of the national survey is summarized in a quality declaration - https://www.havochvatten.se/download/18.619e9cdf163fb20d0dd815a1/1529477995525/kvalitetsdeklaration-2017.pdf . QC of the Site visiting studies is described in the final reports of each projects - https://www.slu.se/globalassets/ew/org/inst/aqua/externwebb/sidan-publikationer/aqua-reports-xxxx_xx/aquarapporter/2018/aqua-reports-2018_22.pdf. The methods carried out on the basis of EU data collection regulations, including the pilot projects, are also evaluated by ICES working group WGRFS.
Monitoring programmes are coordinated and developed in consultation with ICES Working Groups on Salmon in the Baltic Sea (WGBAST) and the Atlantic (WGNAS) and within the EU RCG. The programmes are evaluated by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). In connection with the data being entered into the database, they undergo a quality check. The QC includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Results from electric fishing are reported in digital field protocols that are quality assured in SLU's database Swedish Electricity Fishing Registers (SERS). Quality assurance of age determination (via scales) takes place through recurring international calibrations.
Monitoring programmes are coordinated and developed in consultation with ICES Working Groups on Salmon in the Baltic Sea (WGBAST) and the Atlantic (WGNAS) and within the EU RCG. The programmes are evaluated by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). In connection with the data being entered into the database, they undergo a quality check. The QC includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Results from electric fishing are reported in digital field protocols that are quality assured in SLU's database Swedish Electricity Fishing Registers (SERS). Quality assurance of age determination (via scales) takes place through recurring international calibrations.
The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf
The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf
The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf
The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf
The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf
The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf
The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf
The quality assurance is conducted by strictly following standardized methodology. Quality control takes place within the data hosting for coastal fish. Data is quality checked electronically via a sequence of routine questions and approved manually after a controller specially appointed for the purpose has approved the quality of the material. See also Quality guide for SLU's environmental data management: https://internt.slu.se/globalassets/mw/foma/verksamhetsstod/miljodatastod/kvalitetsguidesdokument/kvalitetsguiden-version-2.4.pdf
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.
For monitoring the health condition of coastal fish, there is a quality declaration that includes the organization, division of responsibilities and quality routines for the monitoring activities. Capture, sampling procedures, analyzes (biochemical, physiological, histological and pathological measurement variables) and data management take place in a standardized manner and follow prepared method instructions. Most of the sampling routines and analysis methods included in the method standard ”Hälsotillstånd hos kustfisk” are covered by accreditation by Swedac.
For monitoring the health condition of coastal fish, there is a quality declaration that includes the organization, division of responsibilities and quality routines for the monitoring activities. Capture, sampling procedures, analyzes (biochemical, physiological, histological and pathological measurement variables) and data management take place in a standardized manner and follow prepared method instructions. Most of the sampling routines and analysis methods included in the method standard ”Hälsotillstånd hos kustfisk” are covered by accreditation by Swedac.
For monitoring the health condition of coastal fish, there is a quality declaration that includes the organization, division of responsibilities and quality routines for the monitoring activities. Capture, sampling procedures, analyzes (biochemical, physiological, histological and pathological measurement variables) and data management take place in a standardized manner and follow prepared method instructions. Most of the sampling routines and analysis methods included in the method standard ”Hälsotillstånd hos kustfisk” are covered by accreditation by Swedac.
For monitoring the health condition of coastal fish, there is a quality declaration that includes the organization, division of responsibilities and quality routines for the monitoring activities. Capture, sampling procedures, analyzes (biochemical, physiological, histological and pathological measurement variables) and data management take place in a standardized manner and follow prepared method instructions. Most of the sampling routines and analysis methods included in the method standard ”Hälsotillstånd hos kustfisk” are covered by accreditation by Swedac.
Data management
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se
On SwAM's website, you can freely search for available data on catch statistics for commercial fishing and daily fishing. Financial data are presented annually in the Annual Economic Reports.
On SwAM's website, you can freely search for available data on catch statistics for commercial fishing and daily fishing. Financial data are presented annually in the Annual Economic Reports.
Electricity fishing data is stored and made publicly accessible via the Electricity Fisheries Register. Raw data from smolt traps are stored in ”Sötebasen” (database under construction at SLU Aqua). There is no national database for fish counters yet. Other information collected is stored in smaller databases at SLU Aqua, from which data can be obtained on request. Swedish data used internationally is delivered to relevant working groups within ICES. Aggregated data from commercial fishing for salmon are stored in ICES database InterCatch.
Electricity fishing data is stored and made publicly accessible via the Electricity Fisheries Register. Raw data from smolt traps are stored in ”Sötebasen” (database under construction at SLU Aqua). There is no national database for fish counters yet. Other information collected is stored in smaller databases at SLU Aqua, from which data can be obtained on request. Swedish data used internationally is delivered to relevant working groups within ICES. Aggregated data from commercial fishing for salmon are stored in ICES database InterCatch.
The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.
The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.
The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.
The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.
The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.
The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.
The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.
The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.
Data access
Related indicator/name
  • ANSSE-2.1A_Intro_fr�mmande_art
  • ANSSE-C.1.1_Intro_fr�mmande_art
  • BALSE-2.1A_Intro_fr�mmande_art
  • BALSE-C.1.1_Intro_fr�mmande_art
  • ANSSE-2.1A_Intro_fr�mmande_art
  • ANSSE-C.1.1_Intro_fr�mmande_art
  • BALSE-2.1A_Intro_fr�mmande_art
  • BALSE-C.1.1_Intro_fr�mmande_art
  • ANSSE-2.1A_Intro_fr�mmande_art
  • ANSSE-C.1.1_Intro_fr�mmande_art
  • BALSE-2.1A_Intro_fr�mmande_art
  • BALSE-C.1.1_Intro_fr�mmande_art
  • ANSSE-2.1A_Intro_fr�mmande_art
  • ANSSE-C.1.1_Intro_fr�mmande_art
  • BALSE-2.1A_Intro_fr�mmande_art
  • BALSE-C.1.1_Intro_fr�mmande_art
  • ANSSE-2.1A_Intro_fr�mmande_art
  • ANSSE-C.1.1_Intro_fr�mmande_art
  • BALSE-2.1A_Intro_fr�mmande_art
  • BALSE-C.1.1_Intro_fr�mmande_art
  • ANSSE-2.1A_Intro_fr�mmande_art
  • ANSSE-C.1.1_Intro_fr�mmande_art
  • BALSE-2.1A_Intro_fr�mmande_art
  • BALSE-C.1.1_Intro_fr�mmande_art
  • ANSSE-2.1A_Intro_fr�mmande_art
  • ANSSE-C.1.1_Intro_fr�mmande_art
  • BALSE-2.1A_Intro_fr�mmande_art
  • BALSE-C.1.1_Intro_fr�mmande_art
  • ANSSE-2.1A_Intro_fr�mmande_art
  • ANSSE-C.1.1_Intro_fr�mmande_art
  • BALSE-2.1A_Intro_fr�mmande_art
  • BALSE-C.1.1_Intro_fr�mmande_art
  • ANSSE-2.1A_Intro_fr�mmande_art
  • ANSSE-C.1.1_Intro_fr�mmande_art
  • BALSE-2.1A_Intro_fr�mmande_art
  • BALSE-C.1.1_Intro_fr�mmande_art
  • BALSE-1.1A_Bif�ngst_tumlare
  • BALSE-1.1A_Bif�ngst_tumlare
  • ANSSE-3.1A_Fiskerid�dlighet
  • ANSSE-C.3.1_Fiskerid�dlighet
  • BALSE-3.1A_Fiskerid�dlighet
  • BALSE-C.3.1_Fiskerid�dlighet
  • ANSSE-3.1A_Fiskerid�dlighet
  • ANSSE-C.3.1_Fiskerid�dlighet
  • BALSE-3.1A_Fiskerid�dlighet
  • BALSE-C.3.1_Fiskerid�dlighet
  • ANSSE-C.3.3_H�llbart_nyttjande_arter
  • BALSE-C.3.3_H�llbart_nyttjande_arter
  • ANSSE-C.3.3_H�llbart_nyttjande_arter
  • BALSE-C.3.3_H�llbart_nyttjande_arter
  • ANSSE-3.1A_Fiskerid�dlighet
  • ANSSE-C.3.1_Fiskerid�dlighet
  • BALSE-3.1A_Fiskerid�dlighet
  • BALSE-C.3.1_Fiskerid�dlighet
  • ANSSE-3.1A_Fiskerid�dlighet
  • ANSSE-C.3.1_Fiskerid�dlighet
  • BALSE-3.1A_Fiskerid�dlighet
  • BALSE-C.3.1_Fiskerid�dlighet
  • ANSSE-8.2D_Reproduktion_t�nglake
  • BALSE-8.2D_Reproduktion_t�nglake
  • ANSSE-8.2D_Reproduktion_t�nglake
  • BALSE-8.2D_Reproduktion_t�nglake
  • ANSSE-8.2D_Reproduktion_t�nglake
  • BALSE-8.2D_Reproduktion_t�nglake
  • ANSSE-8.2D_Reproduktion_t�nglake
  • BALSE-8.2D_Reproduktion_t�nglake
Contact
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
References