Art11

Member State report / Art11 / 2020 / D3 / Baltic

Report type	Member State report to Commission
MSFD Article	Art. 11 Monitoring programmes (and Art. 17 updates)
Report due	2020-10-15
GES Descriptor	D3 Commercial fish and shellfish
Region/subregion	Baltic

Simplified table

Member state	DE	DE	DE	DE	DE	DE	DE	DE	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	DK	EE	EE	EE	FI	FI	LT	LV	LV	LV	PL	SE	SE	SE	SE	SE	SE	SE	SE
Report Access	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL	BAL
Descriptor	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3
Monitoring strategy description	Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen Fischerei in der Ostsee. Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die Auswirkung von Fischerei (D3). Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhalb von D3. Die Monitoringstrategie zu D3 kann in Bezug zur Risikoabschätzung als gestuft bezeichnet werden: Für die wichtigsten, datenreichen Fisch- und Schalentierbestände sind die Messprogramme umfangreich und somit ist die Datengrundlage in vielen Fällen gut. Trotzdem sind die aus diesen Daten abgeleiteten Bewertungen mit Unsicherheiten behaftet, da abgeleitete Parameter natürlichen Schwankungen sowie Beobachtungsungenauigkeiten unterliegen. Für datenarme Bestände ist die Monitoringstrategie als risikoreich zu bezeichnen, da die erhobenen Daten in vielen Fällen keine aussagekräftige Bewertung erlauben. Allerdings ist zu erwähnen, dass eine bessere Monitoringabdeckung in vielen Fällen aus technischer oder personeller Sicht nicht möglich ist oder unverhältnismäßig wäre. Durch das vorhandene Monitoring kann die Wirksamkeit von Maßnahmen bewertet werden.	Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen Fischerei in der Ostsee. Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die Auswirkung von Fischerei (D3). Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhalb von D3. Die Monitoringstrategie zu D3 kann in Bezug zur Risikoabschätzung als gestuft bezeichnet werden: Für die wichtigsten, datenreichen Fisch- und Schalentierbestände sind die Messprogramme umfangreich und somit ist die Datengrundlage in vielen Fällen gut. Trotzdem sind die aus diesen Daten abgeleiteten Bewertungen mit Unsicherheiten behaftet, da abgeleitete Parameter natürlichen Schwankungen sowie Beobachtungsungenauigkeiten unterliegen. Für datenarme Bestände ist die Monitoringstrategie als risikoreich zu bezeichnen, da die erhobenen Daten in vielen Fällen keine aussagekräftige Bewertung erlauben. Allerdings ist zu erwähnen, dass eine bessere Monitoringabdeckung in vielen Fällen aus technischer oder personeller Sicht nicht möglich ist oder unverhältnismäßig wäre. Durch das vorhandene Monitoring kann die Wirksamkeit von Maßnahmen bewertet werden.	Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen Fischerei in der Ostsee. Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die Auswirkung von Fischerei (D3). Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhalb von D3. Die Monitoringstrategie zu D3 kann in Bezug zur Risikoabschätzung als gestuft bezeichnet werden: Für die wichtigsten, datenreichen Fisch- und Schalentierbestände sind die Messprogramme umfangreich und somit ist die Datengrundlage in vielen Fällen gut. Trotzdem sind die aus diesen Daten abgeleiteten Bewertungen mit Unsicherheiten behaftet, da abgeleitete Parameter natürlichen Schwankungen sowie Beobachtungsungenauigkeiten unterliegen. Für datenarme Bestände ist die Monitoringstrategie als risikoreich zu bezeichnen, da die erhobenen Daten in vielen Fällen keine aussagekräftige Bewertung erlauben. Allerdings ist zu erwähnen, dass eine bessere Monitoringabdeckung in vielen Fällen aus technischer oder personeller Sicht nicht möglich ist oder unverhältnismäßig wäre. Durch das vorhandene Monitoring kann die Wirksamkeit von Maßnahmen bewertet werden.	Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen Fischerei in der Ostsee. Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die Auswirkung von Fischerei (D3). Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhalb von D3. Die Monitoringstrategie zu D3 kann in Bezug zur Risikoabschätzung als gestuft bezeichnet werden: Für die wichtigsten, datenreichen Fisch- und Schalentierbestände sind die Messprogramme umfangreich und somit ist die Datengrundlage in vielen Fällen gut. Trotzdem sind die aus diesen Daten abgeleiteten Bewertungen mit Unsicherheiten behaftet, da abgeleitete Parameter natürlichen Schwankungen sowie Beobachtungsungenauigkeiten unterliegen. Für datenarme Bestände ist die Monitoringstrategie als risikoreich zu bezeichnen, da die erhobenen Daten in vielen Fällen keine aussagekräftige Bewertung erlauben. Allerdings ist zu erwähnen, dass eine bessere Monitoringabdeckung in vielen Fällen aus technischer oder personeller Sicht nicht möglich ist oder unverhältnismäßig wäre. Durch das vorhandene Monitoring kann die Wirksamkeit von Maßnahmen bewertet werden.	Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen Fischerei in der Ostsee. Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die Auswirkung von Fischerei (D3). Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhalb von D3. Die Monitoringstrategie zu D3 kann in Bezug zur Risikoabschätzung als gestuft bezeichnet werden: Für die wichtigsten, datenreichen Fisch- und Schalentierbestände sind die Messprogramme umfangreich und somit ist die Datengrundlage in vielen Fällen gut. Trotzdem sind die aus diesen Daten abgeleiteten Bewertungen mit Unsicherheiten behaftet, da abgeleitete Parameter natürlichen Schwankungen sowie Beobachtungsungenauigkeiten unterliegen. Für datenarme Bestände ist die Monitoringstrategie als risikoreich zu bezeichnen, da die erhobenen Daten in vielen Fällen keine aussagekräftige Bewertung erlauben. Allerdings ist zu erwähnen, dass eine bessere Monitoringabdeckung in vielen Fällen aus technischer oder personeller Sicht nicht möglich ist oder unverhältnismäßig wäre. Durch das vorhandene Monitoring kann die Wirksamkeit von Maßnahmen bewertet werden.	Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen Fischerei in der Ostsee. Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die Auswirkung von Fischerei (D3). Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhalb von D3. Die Monitoringstrategie zu D3 kann in Bezug zur Risikoabschätzung als gestuft bezeichnet werden: Für die wichtigsten, datenreichen Fisch- und Schalentierbestände sind die Messprogramme umfangreich und somit ist die Datengrundlage in vielen Fällen gut. Trotzdem sind die aus diesen Daten abgeleiteten Bewertungen mit Unsicherheiten behaftet, da abgeleitete Parameter natürlichen Schwankungen sowie Beobachtungsungenauigkeiten unterliegen. Für datenarme Bestände ist die Monitoringstrategie als risikoreich zu bezeichnen, da die erhobenen Daten in vielen Fällen keine aussagekräftige Bewertung erlauben. Allerdings ist zu erwähnen, dass eine bessere Monitoringabdeckung in vielen Fällen aus technischer oder personeller Sicht nicht möglich ist oder unverhältnismäßig wäre. Durch das vorhandene Monitoring kann die Wirksamkeit von Maßnahmen bewertet werden.	Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen Fischerei in der Ostsee. Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die Auswirkung von Fischerei (D3). Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhalb von D3. Die Monitoringstrategie zu D3 kann in Bezug zur Risikoabschätzung als gestuft bezeichnet werden: Für die wichtigsten, datenreichen Fisch- und Schalentierbestände sind die Messprogramme umfangreich und somit ist die Datengrundlage in vielen Fällen gut. Trotzdem sind die aus diesen Daten abgeleiteten Bewertungen mit Unsicherheiten behaftet, da abgeleitete Parameter natürlichen Schwankungen sowie Beobachtungsungenauigkeiten unterliegen. Für datenarme Bestände ist die Monitoringstrategie als risikoreich zu bezeichnen, da die erhobenen Daten in vielen Fällen keine aussagekräftige Bewertung erlauben. Allerdings ist zu erwähnen, dass eine bessere Monitoringabdeckung in vielen Fällen aus technischer oder personeller Sicht nicht möglich ist oder unverhältnismäßig wäre. Durch das vorhandene Monitoring kann die Wirksamkeit von Maßnahmen bewertet werden.	Das Monitoring kommerziell genutzten Fischbestände erfasst die Abundanz und biologische Parameter einzelner Bestände sowie die Fangzusammensetzungen in der kommerziellen Fischerei in der Ostsee. Das Monitoring erfasst somit Zustände von Fischbeständen, Fischgemeinschaften und die Auswirkung von Fischerei (D3). Die Erfassung der kommerziellen Fänge und die wissenschaftliche Untersuchung von Fischpopulationen/-Beständen erlaubt die Abschätzung von Fangempfehlungen entsprechend des MSY-Ansatzes. Der MSY-Ansatz ist die Basis für die GES-Festlegung innerhalb von D3. Die Monitoringstrategie zu D3 kann in Bezug zur Risikoabschätzung als gestuft bezeichnet werden: Für die wichtigsten, datenreichen Fisch- und Schalentierbestände sind die Messprogramme umfangreich und somit ist die Datengrundlage in vielen Fällen gut. Trotzdem sind die aus diesen Daten abgeleiteten Bewertungen mit Unsicherheiten behaftet, da abgeleitete Parameter natürlichen Schwankungen sowie Beobachtungsungenauigkeiten unterliegen. Für datenarme Bestände ist die Monitoringstrategie als risikoreich zu bezeichnen, da die erhobenen Daten in vielen Fällen keine aussagekräftige Bewertung erlauben. Allerdings ist zu erwähnen, dass eine bessere Monitoringabdeckung in vielen Fällen aus technischer oder personeller Sicht nicht möglich ist oder unverhältnismäßig wäre. Durch das vorhandene Monitoring kann die Wirksamkeit von Maßnahmen bewertet werden.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	Overvågningsprogrammet for de erhvervsmæssigt udnyttede fiskebestande skal skabe grundlag for en løbende vurdering af tilstanden, så det kan vurderes om populationerne af alle fiske- og skaldyrar-ter, der udnyttes erhvervsmæssigt, ligger inden for sikre biologiske grænser og udvise en alders- og størrelsesfordeling, der er betegnende for en sund bestand. Deskriptoren omhandler de fiskebestande, der fiskes i både konsum- og industrifiskeriet, hvorved de betegnes som erhvervsmæssigt udnyttede. Disse arter udgør en stor andel af havets samlede bio-masse og udfylder vigtige roller i havmiljøet som fødeemner og toprovdyr. En god miljøtilstand i havet, som er forenelig med et bæredygtigt fiskeri er således afhængig af, at disse bestande er sunde i deres forekomst og udbredelse. I de danske havområder forvaltes de erhvervsmæssigt udnyttede fiskebestande i henhold til den fæl-les fiskeripolitik i EU-regi. Forvaltningen bygger på videnskabelig rådgivning fra ICES (Det Internati-onale Havundersøgelsesråd) og DTU Aqua (Institut for Akvatiske Ressourcer), der benyttes til fast-sættelse af kvoter på EU-niveau og som efterfølgende fordeles mellem medlemslandene efter aftalte fordelingsnøgler. Kvoterne fastsættes efter principper om et maksimalt bæredygtigt udbytte (Maximum Sustainable Yield, MSY) med referencepunkter fastsat ud fra forsigtighedsprincippet. Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.	The aim of the monitoring strategy "SD3 – Commercially exploited fish" is to assess the status of main commercial fish species in the sea areas of Estonia. The strategy aims to contribute to the assessment of the fishing mortality, status of spawning stock biomass and size and age structure of monitored stocks. The monitored fish stocks include pelagic Baltic herring (two stocks) and sprat stocks, economically significant coastal fish species (perch, flounder, pikeperch) and Atlantic salmon is used as an indicator species for migratory (anadromous) fishes. The monitoring is undertaken under the "Coastal fish" and "Off-shore fish" monitoring programmes. The data on human activities that potentially affect fish stocks are collected in the programme “Marine and coastal activities”. An additional data indirectly contributing to the strategy is gathered from several monitoring programmes as "Non-indigenous species – harbours and adjacent regions", "Inputs of nutrients and contaminants – land-based sources", "Contaminant levels – in sediment", "Contaminant levels – in water", "Oil spills", "Macrolitter", "Litter micro-particles", "Impulsive underwater noise" and "Continuous underwater noise".	The aim of the monitoring strategy "SD3 – Commercially exploited fish" is to assess the status of main commercial fish species in the sea areas of Estonia. The strategy aims to contribute to the assessment of the fishing mortality, status of spawning stock biomass and size and age structure of monitored stocks. The monitored fish stocks include pelagic Baltic herring (two stocks) and sprat stocks, economically significant coastal fish species (perch, flounder, pikeperch) and Atlantic salmon is used as an indicator species for migratory (anadromous) fishes. The monitoring is undertaken under the "Coastal fish" and "Off-shore fish" monitoring programmes. The data on human activities that potentially affect fish stocks are collected in the programme “Marine and coastal activities”. An additional data indirectly contributing to the strategy is gathered from several monitoring programmes as "Non-indigenous species – harbours and adjacent regions", "Inputs of nutrients and contaminants – land-based sources", "Contaminant levels – in sediment", "Contaminant levels – in water", "Oil spills", "Macrolitter", "Litter micro-particles", "Impulsive underwater noise" and "Continuous underwater noise".	The aim of the monitoring strategy "SD3 – Commercially exploited fish" is to assess the status of main commercial fish species in the sea areas of Estonia. The strategy aims to contribute to the assessment of the fishing mortality, status of spawning stock biomass and size and age structure of monitored stocks. The monitored fish stocks include pelagic Baltic herring (two stocks) and sprat stocks, economically significant coastal fish species (perch, flounder, pikeperch) and Atlantic salmon is used as an indicator species for migratory (anadromous) fishes. The monitoring is undertaken under the "Coastal fish" and "Off-shore fish" monitoring programmes. The data on human activities that potentially affect fish stocks are collected in the programme “Marine and coastal activities”. An additional data indirectly contributing to the strategy is gathered from several monitoring programmes as "Non-indigenous species – harbours and adjacent regions", "Inputs of nutrients and contaminants – land-based sources", "Contaminant levels – in sediment", "Contaminant levels – in water", "Oil spills", "Macrolitter", "Litter micro-particles", "Impulsive underwater noise" and "Continuous underwater noise".	The vast majority of monitoring data on the main commercial species is collected in the EU Fisheries Data Collection Programme. Data will be collected for analysis and advice in support of the EUâs Common Fisheries Policy. The Data Collection Programme collects data on the status of herring, sprat, cod and salmon stocks, among others. Data on these species will be analysed and reported as international cooperation in the working groups of the International Council for the Exploration of the Sea (ICES). ICES has also made preliminary assessments and recommendations on the implementation of farm estimates for Descriptor 3 (ICES 2014). In addition to the EU Data Collection Programme, data are also produced for catch statistics for commercial fisheries. In addition to the stocks assessed through international cooperation, some of the so-called coastal species are also important species for commercial fishing. In particular, there would be a need for more systematic monitoring data on the status of spikes and pigs in coastal waters. Fishing is the most important factor in the state of commercial species. In addition to commercial fishing, recreational fishing also plays an important role in coastal populations. The programme provides information to MSFD descriptor 1 (D1C1, D1C2 and D1C3), descriptor 3 (D3C1, D3C2 and D3C3) and descriptor 4 (D4C1, D4C2). The programme also collects data on fisheries under pressure.	The vast majority of monitoring data on the main commercial species is collected in the EU Fisheries Data Collection Programme. Data will be collected for analysis and advice in support of the EUâs Common Fisheries Policy. The Data Collection Programme collects data on the status of herring, sprat, cod and salmon stocks, among others. Data on these species will be analysed and reported as international cooperation in the working groups of the International Council for the Exploration of the Sea (ICES). ICES has also made preliminary assessments and recommendations on the implementation of farm estimates for Descriptor 3 (ICES 2014). In addition to the EU Data Collection Programme, data are also produced for catch statistics for commercial fisheries. In addition to the stocks assessed through international cooperation, some of the so-called coastal species are also important species for commercial fishing. In particular, there would be a need for more systematic monitoring data on the status of spikes and pigs in coastal waters. Fishing is the most important factor in the state of commercial species. In addition to commercial fishing, recreational fishing also plays an important role in coastal populations. The programme provides information to MSFD descriptor 1 (D1C1, D1C2 and D1C3), descriptor 3 (D3C1, D3C2 and D3C3) and descriptor 4 (D4C1, D4C2). The programme also collects data on fisheries under pressure.	Verslinių žuvų rūšių (menkė, strimelė, brėtlingis ir plekšnė) duomenys renkami pagal Lietuvos nacionalinės žuvininkystės duomenų rinkimo programą. Pagal gautus duomenis, ICES skaičiuoja vertes D3C1 ir D3C2 kriterijų rodikliams (mirtingumo dėl žvejybos koeficientas (F) ir neršiančių išteklių biomasė (SSB) atskiriems Baltijos jūros pakvadračiams. Nacionaliniu lygiu skaičiuojamos vertės D3C3 kriterijaus rodikliams: 1) populiacijos pasiskirstymas pagal amžių ir dydį ir 2) didesnių už vidutinę pirmos lytinės brandos normą žuvų proporcija. Tyrimai pagal Duomenų rinkimo programą vykdomi 4 kartus per metus. Du kartai dugniniu tralu menkės ir plekšnės rodikliams skaičiuoti ir 2 kartai akustikos tyrimai strimelių ir brėtlingių rodikliams skaičiuoti. D3C1 rodiklio skaičiavimui taip pat renkama biologiniai mėginiai iš verslinių laimikių. Verslinių mėginių rinkimas priklauso nuo žvejybos laiko ir intensyvumo. Verslinių mėginių ėmimas vyksta du kartus per mėnesį kiekvienai verslinei rūšiai, jei vyksta žvejyba.	Data are acquired in accordance with EPP regulation (EU) 2017/1004, EK decision (EU) 2019/909 and delegated decision (EU) 2019/910.	Data are acquired in accordance with EPP regulation (EU) 2017/1004, EK decision (EU) 2019/909 and delegated decision (EU) 2019/910.	Data are acquired in accordance with EPP regulation (EU) 2017/1004, EK decision (EU) 2019/909 and delegated decision (EU) 2019/910.	Within the strategy information on the population dynamics of commercially exploited fish stocks is gathered. This strategy aims at providing data for assessments of the status of marine waters according to the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017 and to assess human impact on exploited fish stocks as well as effectiveness of measures applied. Regional coordination is assured by applying ICES common monitoring guidelines SISP manual for the Baltic International Trawl Surveys (BITS) and SISP Manual of international Baltic acoustic surveys (IBAS) and monitor commonly agreed fish stocks.	Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries. Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon)	Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries. Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon)	Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries. Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon)	Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries. Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon)	Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries. Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon)	Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries. Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon)	Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries. Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon)	Monitoring follow the requirements in the CFP and DCF to provide data for assessing status and for ICES and STECF advices. Monitoring of fish and fisheries helps to assess the progress with the relevant targets and measures, since the targets has indicators backed up with data and the measures are specifically targeting fisheries. Comment: ANSSE-0024 and BALSE-0024 was not available in the list, but is also relevant here (salmon)
Coverage of GES criteria	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014	Adequate monitoring was in place in 2014
Gaps and plans	Eine adäquate Überwachung besteht seit 2014	Eine adäquate Überwachung besteht seit 2014	Eine adäquate Überwachung besteht seit 2014	Eine adäquate Überwachung besteht seit 2014	Eine adäquate Überwachung besteht seit 2014	Eine adäquate Überwachung besteht seit 2014	Eine adäquate Überwachung besteht seit 2014	Eine adäquate Überwachung besteht seit 2014	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	Overvågningsprogrammet er tilstrækkeligt.	There are no evident gaps or shortcomings in the commercially exploited fish monitoring strategy.	There are no evident gaps or shortcomings in the commercially exploited fish monitoring strategy.	There are no evident gaps or shortcomings in the commercially exploited fish monitoring strategy.	Monitoring of some coastal species requires development but the monitoring is still seen adequate to assess state of coastal fish.	Monitoring of some coastal species requires development but the monitoring is still seen adequate to assess state of coastal fish.	Manome, kad monitoringas yra pakankamas.	None	None	None	Not applicable	Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1).	Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1).	Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1).	Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1).	Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1).	Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1).	Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1).	Monitoring within the Common Fisheries Policy (CFP) provides a good basis for assessing both fishing mortality (D3C1) and spawning biomass (D3C2). Data for assessment of size distribution at stock level (D3C3) are also available. However, there are data gaps for non-target species, such as elasmobranches on the West Coast, see gaps and plans in the fish monitoring strategy (Descriptor 1).
Related targets	UZO4 UZO4.1 UZO4.2 UZO4.4	UZO4 UZO4.1 UZO4.2 UZO4.4	UZO4 UZO4.1 UZO4.2 UZO4.4	UZO4 UZO4.1 UZO4.2 UZO4.4	UZO4 UZO4.1 UZO4.2 UZO4.4	UZO4 UZO4.1 UZO4.2 UZO4.4	UZO4 UZO4.1 UZO4.2 UZO4.4	UZO4 UZO4.1 UZO4.2 UZO4.4													BALEE-T30 BALEE-T33 BALEE-T34 BALEE-T36 Target 10 Target 11 Target 16 Target 19 Target 23 Target 26 Target 8	BALEE-T30 BALEE-T33 BALEE-T34 BALEE-T36 Target 10 Target 11 Target 16 Target 19 Target 23 Target 26 Target 8	BALEE-T30 BALEE-T33 BALEE-T34 BALEE-T36 Target 10 Target 11 Target 16 Target 19 Target 23 Target 26 Target 8	LUVA1 LUVAyleinen	LUVA1 LUVAyleinen	1	JVM2	JVM2	JVM2	PL_Target_D3 PL_Target_D3C1 PL_Target_D3C2 PL_Target_D3C3 PL_Target_D3_Cod 24-32 PL_Target_D3_Flounder 24-25 PL_Target_D3_Herring 25-29 and 32 Ex GoR PL_Target_D3_Sprat 22-32	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 is in place by July 2020	Adequate monitoring was in 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	BALDE-M411-UZ4-01 - 'Weitere Verankerung des Themas „nachhaltige ökosystemgerechte Fischerei“ im öffentlichen Bewusstsein' BALDE-M412-UZ4-02 - 'Fischereimaßnahmen' BALDE-M926-other - 'Umsetzung der neuen Gemeinsame Fischereipolitik (GFP)' BALDE-M927-other - 'Umsetzung der Regelungen in den Landesfischereigesetzen' BALDE-M929-other - 'Integriertes Küstenzonenmanagement'	BALDE-M411-UZ4-01 - 'Weitere Verankerung des Themas „nachhaltige ökosystemgerechte Fischerei“ im öffentlichen Bewusstsein' BALDE-M412-UZ4-02 - 'Fischereimaßnahmen' BALDE-M926-other - 'Umsetzung der neuen Gemeinsame Fischereipolitik (GFP)' BALDE-M927-other - 'Umsetzung der Regelungen in den Landesfischereigesetzen' BALDE-M929-other - 'Integriertes Küstenzonenmanagement'	BALDE-M411-UZ4-01 - 'Weitere Verankerung des Themas „nachhaltige ökosystemgerechte Fischerei“ im öffentlichen Bewusstsein' BALDE-M412-UZ4-02 - 'Fischereimaßnahmen' BALDE-M926-other - 'Umsetzung der neuen Gemeinsame Fischereipolitik (GFP)' BALDE-M927-other - 'Umsetzung der Regelungen in den Landesfischereigesetzen' BALDE-M929-other - 'Integriertes Küstenzonenmanagement'	BALDE-M411-UZ4-01 - 'Weitere Verankerung des Themas „nachhaltige ökosystemgerechte Fischerei“ im öffentlichen Bewusstsein' BALDE-M412-UZ4-02 - 'Fischereimaßnahmen' BALDE-M926-other - 'Umsetzung der neuen Gemeinsame Fischereipolitik (GFP)' BALDE-M927-other - 'Umsetzung der Regelungen in den Landesfischereigesetzen' BALDE-M929-other - 'Integriertes Küstenzonenmanagement'	BALDE-M411-UZ4-01 - 'Weitere Verankerung des Themas „nachhaltige ökosystemgerechte Fischerei“ im öffentlichen Bewusstsein' BALDE-M412-UZ4-02 - 'Fischereimaßnahmen' BALDE-M926-other - 'Umsetzung der neuen Gemeinsame Fischereipolitik (GFP)' BALDE-M927-other - 'Umsetzung der Regelungen in den Landesfischereigesetzen' BALDE-M929-other - 'Integriertes Küstenzonenmanagement'	BALDE-M411-UZ4-01 - 'Weitere Verankerung des Themas „nachhaltige ökosystemgerechte Fischerei“ im öffentlichen Bewusstsein' BALDE-M412-UZ4-02 - 'Fischereimaßnahmen' BALDE-M926-other - 'Umsetzung der neuen Gemeinsame Fischereipolitik (GFP)' BALDE-M927-other - 'Umsetzung der Regelungen in den Landesfischereigesetzen' BALDE-M929-other - 'Integriertes Küstenzonenmanagement'	BALDE-M411-UZ4-01 - 'Weitere Verankerung des Themas „nachhaltige ökosystemgerechte Fischerei“ im öffentlichen Bewusstsein' BALDE-M412-UZ4-02 - 'Fischereimaßnahmen' BALDE-M926-other - 'Umsetzung der neuen Gemeinsame Fischereipolitik (GFP)' BALDE-M927-other - 'Umsetzung der Regelungen in den Landesfischereigesetzen' BALDE-M929-other - 'Integriertes Küstenzonenmanagement'	BALDE-M411-UZ4-01 - 'Weitere Verankerung des Themas „nachhaltige ökosystemgerechte Fischerei“ im öffentlichen Bewusstsein' BALDE-M412-UZ4-02 - 'Fischereimaßnahmen' BALDE-M926-other - 'Umsetzung der neuen Gemeinsame Fischereipolitik (GFP)' BALDE-M927-other - 'Umsetzung der Regelungen in den Landesfischereigesetzen' BALDE-M929-other - 'Integriertes Küstenzonenmanagement'													BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M005 - 'Developing regional fishing restrictions and updating the size limits of commercial fish' BALEE-M006 - 'Supporting the marketing/the use of limited value fish' BALEE-M007 - 'Adjusting the fishing effort not to compromise achieving GES' BALEE-M008 - 'Application of electronic reporting system for fishing gears to better control fishing and avoid abandoning of fishing gear' Not specified - 'European Maritime and Fisheries Fund (EMFF) Operational Programme for Estonia 2014-2020'	BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M005 - 'Developing regional fishing restrictions and updating the size limits of commercial fish' BALEE-M006 - 'Supporting the marketing/the use of limited value fish' BALEE-M007 - 'Adjusting the fishing effort not to compromise achieving GES' BALEE-M008 - 'Application of electronic reporting system for fishing gears to better control fishing and avoid abandoning of fishing gear' Not specified - 'European Maritime and Fisheries Fund (EMFF) Operational Programme for Estonia 2014-2020'	BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M005 - 'Developing regional fishing restrictions and updating the size limits of commercial fish' BALEE-M006 - 'Supporting the marketing/the use of limited value fish' BALEE-M007 - 'Adjusting the fishing effort not to compromise achieving GES' BALEE-M008 - 'Application of electronic reporting system for fishing gears to better control fishing and avoid abandoning of fishing gear' Not specified - 'European Maritime and Fisheries Fund (EMFF) Operational Programme for Estonia 2014-2020'	BALFI-M011-FISH - 'FISH1 - Assessment of the possibilities and need for improving the effectiveness of restrictions on fishing of coastal species'	BALFI-M011-FISH - 'FISH1 - Assessment of the possibilities and need for improving the effectiveness of restrictions on fishing of coastal species'						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-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-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-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-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-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-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-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-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-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-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-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-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-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-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-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-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
Related monitoring programmes	BALDE_MPr_119_MP_086 BALDE_MPr_119_MP_137 BALDE_MPr_121_MP_077 BALDE_MPr_121_MP_079 BALDE_MPr_121_MP_082 BALDE_MPr_121_MP_083 BALDE_MPr_121_MP_085 BALDE_MPr_121_MP_089	BALDE_MPr_119_MP_086 BALDE_MPr_119_MP_137 BALDE_MPr_121_MP_077 BALDE_MPr_121_MP_079 BALDE_MPr_121_MP_082 BALDE_MPr_121_MP_083 BALDE_MPr_121_MP_085 BALDE_MPr_121_MP_089	BALDE_MPr_119_MP_086 BALDE_MPr_119_MP_137 BALDE_MPr_121_MP_077 BALDE_MPr_121_MP_079 BALDE_MPr_121_MP_082 BALDE_MPr_121_MP_083 BALDE_MPr_121_MP_085 BALDE_MPr_121_MP_089	BALDE_MPr_119_MP_086 BALDE_MPr_119_MP_137 BALDE_MPr_121_MP_077 BALDE_MPr_121_MP_079 BALDE_MPr_121_MP_082 BALDE_MPr_121_MP_083 BALDE_MPr_121_MP_085 BALDE_MPr_121_MP_089	BALDE_MPr_119_MP_086 BALDE_MPr_119_MP_137 BALDE_MPr_121_MP_077 BALDE_MPr_121_MP_079 BALDE_MPr_121_MP_082 BALDE_MPr_121_MP_083 BALDE_MPr_121_MP_085 BALDE_MPr_121_MP_089	BALDE_MPr_119_MP_086 BALDE_MPr_119_MP_137 BALDE_MPr_121_MP_077 BALDE_MPr_121_MP_079 BALDE_MPr_121_MP_082 BALDE_MPr_121_MP_083 BALDE_MPr_121_MP_085 BALDE_MPr_121_MP_089	BALDE_MPr_119_MP_086 BALDE_MPr_119_MP_137 BALDE_MPr_121_MP_077 BALDE_MPr_121_MP_079 BALDE_MPr_121_MP_082 BALDE_MPr_121_MP_083 BALDE_MPr_121_MP_085 BALDE_MPr_121_MP_089	BALDE_MPr_119_MP_086 BALDE_MPr_119_MP_137 BALDE_MPr_121_MP_077 BALDE_MPr_121_MP_079 BALDE_MPr_121_MP_082 BALDE_MPr_121_MP_083 BALDE_MPr_121_MP_085 BALDE_MPr_121_MP_089	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	DK-D03-01 DK-D03-02 DK-D03-03 DK-D03-04 DK-D03-05 DK-D03-06 DK-D03-07 DK-D03-08 DK-D03-09 DK-D03-10 DK-D03-11 DK-D03-12	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore	BALFI-d03-1 BALFI-d03-2	BALFI-d03-1 BALFI-d03-2	BALLT-D01234_FishOffshore	LV-4.3.1. (D3C1) LV-4.3.2. (D3C2) LV-4.3.3. (D3C3)	LV-4.3.1. (D3C1) LV-4.3.2. (D3C2) LV-4.3.3. (D3C3)	LV-4.3.1. (D3C1) LV-4.3.2. (D3C2) LV-4.3.3. (D3C3)	PL-D1.3-01	SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D3D4D6-seafloormegafauna	SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D3D4D6-seafloormegafauna	SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D3D4D6-seafloormegafauna	SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D3D4D6-seafloormegafauna	SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D3D4D6-seafloormegafauna	SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D3D4D6-seafloormegafauna	SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D3D4D6-seafloormegafauna	SE-D1D3-bycatch SE-D1D3-comfishing SE-D1D3-eel SE-D1D3-recreationalfishing SE-D1D3-salmon SE-D1D3D4-coastalfish SE-D1D3D4-offshorefish SE-D1D3D4D6-seafloormegafauna
Programme code	BALDE_MPr_119_MP_086	BALDE_MPr_119_MP_137	BALDE_MPr_121_MP_077	BALDE_MPr_121_MP_079	BALDE_MPr_121_MP_082	BALDE_MPr_121_MP_083	BALDE_MPr_121_MP_085	BALDE_MPr_121_MP_089	DK-D03-01	DK-D03-02	DK-D03-03	DK-D03-04	DK-D03-05	DK-D03-06	DK-D03-07	DK-D03-08	DK-D03-09	DK-D03-10	DK-D03-11	DK-D03-12	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D010403-7_FishCoastal	BALEE-D010403-8_FishOffshore	BALFI-D03-1	BALFI-D03-2	BALLT-D01234_FishOffshore	LV-4.3.1. (D3C1)	LV-4.3.2. (D3C2)	LV-4.3.3. (D3C3)	PL-D1.3-01	SE-D1D3-bycatch	SE-D1D3-comfishing	SE-D1D3-eel	SE-D1D3-recreationalfishing	SE-D1D3-salmon	SE-D1D3D4-coastalfish	SE-D1D3D4-offshorefish	SE-D1D3D4D6-seafloormegafauna
Programme name	Mobile Arten (Fische) - Sterblichkeits/Schädigungsraten durch Fischerei (gezielt und/oder beiläufig): Beprobung der kommerziellen Fischerei (DCF) - Ostsee	Mobile Arten (Fische) - Sterblichkeits/Schädigungsraten durch Fischerei (gezielt und/oder beiläufig): Data Collection Framework (DCF), Recreational Fisheries (Freizeitfischerei), Ostsee	Mobile Arten (Fische) - Bestandsmerkmale: Baltic International Trawl Survey (BITS), Ostsee	Mobile Arten (Fische) - Bestandsmerkmale: Hydroakustische Bestandsaufnahme pelagischer Fischarten in der westlichen Ostsee (German Autumn Acoustic Survey, GERAS)	Mobile Arten (Fische) - Bestandsmerkmale: Hydroakustik-Survey GerBASS, Ostsee	Mobile Arten (Fische) - Bestandsmerkmale: Rügen Heringslarvensurvey	Mobile Arten (Fische) - Bestandsmerkmale: Reproduktion von Dorsch in der Ostsee (CoBalt)	Mobile Arten (Fische) - Bestandsmerkmale: Effizienzkontrolle Meerforellenbesatz Mecklenburg-Vorpommern	Mobile species - distribution, abundance and/or biomass - demersal fish - Survey IBTS	Mobile species - distribution, abundance and or biomass - demersal fish - Survey BITS	Mobile species - distribution, abundance and or biomass - cod - Survey CODS_Q4	Mobile species - distribution, abundance and or biomass - flatfish - Survey FFS	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) - Observatørture	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) - Fiskerikontrollen	Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) - Fiskerikontrol med kameraovervågning	Mobile species - distribution, abundance and/or biomass - pelagic fish - Survey NHAS	Mobile species - distribution, abundance and/or biomass - pelagic fish - Survey IESNS	Mobile species - distribution, abundance and/or biomass - sandeel - Survey NSSS	Benthic species - abundance and/or biomass - nephrops - Survey NTV3&4	Mobile species - distribution, abundance and/or biomass - pelagic fish - Survey IESSNS	Marine and coastal activities	Coastal fish	Off-shore fish	Fisheries data collection	Commercial fisheries catch statistics	BALLT-D01234_FishOffshore	Mobile species mortality rates from fisheries (commercially-exploited fish species)	Mobile species the spawning stock biomass of populations of commercially-exploited fish species	Mobile species population characteristics (age and size distribution of individuals of populations of commercially-exploited fish species)	Mobile species - fish of the deep-water zone	Bycatch	Commercial fisheries	Migratory fish (eel)	Recreational fisheries	Migratory fish (salmon)	Coastal fish	Offshore fish	Macrozoobenthos - on the seafloor
Update type	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Modified from 2014	Modified from 2014	New programme	Modified from 2014	Modified from 2014	New programme	New programme	Modified from 2014	Modified from 2014	Modified from 2014	New programme	New programme	Modified from 2014	Modified from 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	New programme	New programme	New programme	New programme	Modified from 2014	New programme	Modified from 2014	New programme	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014
Old programme codes	BALDE_Sub_119	BALDE_Sub_119	BALDE_Sub_121	BALDE_Sub_121	BALDE_Sub_121	BALDE_Sub_121	BALDE_Sub_121	BALDE_Sub_121	ANSDK_D01-07a_abund_fish_offshore_demersal	BALDK-D01-07a_abund_fish_offshore_demersal BALDK-D01-14_population_fish_demersal			ANSDK-D03-10_mortal_fish_offsh_commercial BALDK-D03-10_mortal_fish_offsh_commercial			ANSDK-D01-06a_abundance_fish_migratory	ANSDK-D01-06b_abund_fish_migratory_pelagic ANSDK-D03-09_mortal_fish_migrat_pelagic	ANSDK-D01-21_habitat_demersal_sandeel ANSDK_D01-07b_abundance_fish_sandeel			BALEE-D00-39_CoastalOffshoreActivities	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory									ANSSE-COMFISH-D3-Utkast BALSE-COMFISH-D3-Utkast		ANSSE-COMFISH-D314-Al BALSE-COMFISH-D314-Al		BALSE-COMFISH-D314-Lax	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-Havskrafta
Programme description	Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): \|\| BALDE_MP_86 \|\| Beprobung der kommerziellen Fischerei (DCF) - Ostsee \|\| Die Beprobung der Fangzusammensetzung in der kommerziellen Fischerei erfolgt im Rahmen des EU-Datensammelprogramms (DCF/DC-MAP). Die Fangbeprobung ermöglicht die Abschätzung der fischereilich induzierten Sterblichkeit für die Bestandsbewertungen des ICES, welche als Beratungsgrundlagen für die Festlegung von Fangquoten Eingang in die Gemeinsame Fischereipolitik der Europäischen Union (GFP) finden. Die Fangbeprobung wird fortlaufend weiter entwickelt und durch die Gremien des ICES und der EU (STECF) kontrolliert und koordiniert. Neue Beprobungstechniken wie die Videoüberwachung der Fänge werden gerade getestet, allerdings ist unklar, ob und wie diese Techniken in der Lage sind, eine Beprobung durch Personen auf See zu ersetzen. Bisher bieten Beprobungen durch Personen auf See nach wie vor den höchsten Datenstandard, digitale Beprobungstechniken könnten in Zukunft aber den Beprobungsumfang steigern.	Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): \|\| BALDE_MP_137 \|\| Data Collection Framework (DCF), Recreational Fisheries (Freizeitfischerei), Ostsee \|\| Die Beprobung der Fangzusammensetzung in der kommerziellen Fischerei erfolgt im Rahmen des EU-Datensammelprogramms (DCF/DC-MAP). Die Fangbeprobung ermöglicht die Abschätzung der fischereilich induzierten Sterblichkeit für die Bestandsbewertungen des ICES, welche als Beratungsgrundlagen für die Festlegung von Fangquoten Eingang in die Gemeinsame Fischereipolitik der Europäischen Union (GFP) finden. Die Fangbeprobung wird fortlaufend weiter entwickelt und durch die Gremien des ICES und der EU (STECF) kontrolliert und koordiniert. Neue Beprobungstechniken wie die Videoüberwachung der Fänge werden gerade getestet, allerdings ist unklar, ob und wie diese Techniken in der Lage sind, eine Beprobung durch Personen auf See zu ersetzen. Bisher bieten Beprobungen durch Personen auf See nach wie vor den höchsten Datenstandard, digitale Beprobungstechniken könnten in Zukunft aber den Beprobungsumfang steigern.	Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): \|\| BALDE_MP_77 \|\| Baltic International Trawl Survey (BITS), Ostsee \|\| Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).	Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): \|\| BALDE_MP_79 \|\| Hydroakustische Bestandsaufnahme pelagischer Fischarten in der westlichen Ostsee (German Autumn Acoustic Survey, GERAS) \|\| Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).	Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): \|\| BALDE_MP_82 \|\| Hydroakustik-Survey GerBASS, Ostsee \|\| Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).	Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): \|\| BALDE_MP_83 \|\| Rügen Heringslarvensurvey \|\| Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).	Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): \|\| BALDE_MP_85 \|\| Reproduktion von Dorsch in der Ostsee (CoBalt) \|\| Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).	Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): \|\| BALDE_MP_89 \|\| Effizienzkontrolle Meerforellenbesatz Mecklenburg-Vorpommern \|\| Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).Die Bestandsmerkmale (individuelles Alter, Länge, Gewicht, Geschlecht und Reifegrad) werden mit den gleichen Methoden wie die Abundanz und Biomasse von Fischen erfasst. Deswegen gelten die gleichen Eckpunkte der Monitoring-Strategie (internationale Koordination, Standardisierbarkeit, Erhalt der Zeitserie).	IBTS - International Bottom Trawl Survey Dette survey har til formål, at monitere udbredelsen, bestandsstørrelserne og den årlige rekruttering af kommercielt udnyttede fiskebestande I Nordsøen. IBTS finder sted to gange årligt i 1. kvartal i februar (IBTS 1) og i 3. kvartal i august (IBTS). Under dette survey bundtrawles der ved faste lokaliteter og alle fangsterne registreres til art og længde, og yderligere biologiske parametre måles for udvalgte arter (alder, køn, seksuel modenhed). Således indsamles der også data for mindre udbredte fiskearter, der ikke udnyttes erhvervsmæssigt. Desuden indsamles også hydrografiske data med CTD og sildelarver overvåges ved brug af et MIK net (Midwater Ringnet). IBTS er internationalt koordineret igennem ICES arbejdsgruppen IBTSWG og data anvendes af arbejdsgrupperne WGNSSK og HAWG til assessment og rådgivning.	BITS - Baltic International Trawl Survey Dette survey har til formål, at monitere udbredelsen, bestandsstørrelserne og den årlige rekruttering af kommercielt udnyttede fiskebestande i Kattegat, Bælthavet og Østersøen, med særlig fokus på målarterne torsk, skrubbe, rødspætte, brisling og sild. BITS udføres to gange om året i 1. kvartal i marts (BITS 1) og i 4. kvartal i november (BITS 4). Under dette survey bundtrawles der ved faste lokaliteter og alle fangsterne registreres til art og længde, og yderligere biologiske parametre måles for udvalgte arter (alder, køn, seksuel modenhed). Således indsamles der også data for mindre udbredte fiskearter, der ikke udnyttes erhvervsmæssigt. Desuden indsamles der hydrografiske data med CTD, plankton/zooplankton med WP2 net og fiskeæg/fiskelarver med Bongo net. BITS er internationalt koordineret igennem ICES arbejdsgruppen WGBIFS, og data anvendes af arbejdsgruppen WGBFAS til assessment og rådgivning.	CODS_Q4 - Cod survey in 3aS Dette survey har til formål, at monitere udbredelsen, bestandsstørrelserne og den årlige rekruttering af torsk i Kattegat, i supplering til BITS. CODS_Q4 finder sted i 4. kvartal. Under dette survey benyttes et finmasket trawl net (70 mm), og alle fangsterne registreres til art og længde, og yderligere biologiske parametre måles for udvalgte arter (alder, køn, seksuel modenhed). Således indsamles der også data for mindre udbredte fiskearter, der ikke udnyttes erhvervsmæssigt. Desuden indsamles også hydrografiske data med CTD. CODS_Q4 koordineres imellem Danmark og Sverige og ICES arbejdsgruppen WGBFAS anvender data til assessment og rådgivning.	FFS - Flatfish survey in the Kattegat and Skagerrak Dette survey har til formål, at monitere udbredelsen, bestandsstørrelserne og den årlige rekruttering af tunge og rødspætte i Kattegat og Skagerrak. FFS finder sted i 4. kvartal. Under dette survey benyttes et finmasket trawl net (70 mm), og alle fangsterne registreres til art og længde, og yderligere biologiske parametre måles for udvalgte arter (alder, køn, seksuel modenhed). Således indsamles der også data for mindre udbredte fiskearter, der ikke udnyttes erhvervsmæssigt. Desuden indsamles også hydrografiske data med CTD. CODS_Q4 koordineres imellem Danmark og Sverige og ICES arbejdsgruppen WGBFAS anvender data til assessment og rådgivning.	Observatørture DTU Aqua foretager årligt omkring 200 observatørture, hvor observatører registrerer fangstsammen-sætningen på kommercielle fiskefartøjer. Allefangsterne registreres til art og længde, og yderligere biologiske parametre måles for udvalgte arter (længde, alder, køn, seksuel modenhed). Således indsamles der også data for mindre udbredte fiskearter, der ikke udnyttes erhvervsmæssigt. Data fra de videnskabelige observatørture giver information om omfanget af udsmid af erhvervsmæssigt udnyttede arter, hvilket bidrager til en mere eksakt vurdering af fiskeridødeligheden for nogle arter af fisk, der udnyttes erhvervsmæssigt. Derudover registreres bifangst af havpattedyr, fugle, fisk, der ikke udnyttes erhvervsmæssigt og marint affald indsamles og registreres.	Fiskerikontrollen Fiskerikontrollen fører kontrol med det erhvervsmæssige fiskeri ved fysisk kontrol til havs, i havn, ved landing, under transport af fisk og hos opkøbere af fisk. Endvidere foretages der administrativ kontrol af faretøjer og opkøberes indberettede oplysninger. For kvoterede fiskearter er erhvervsfiskere pålagt en landingsforpligtigelse og skal derfor bringe deres fangster i land. Fiskerikontrollen laver på det grundlag en opgørelse af de samlede landinger på artsniveau. Udviklingen i landingstal giver for nogle arter indblik i bestandsudviklingen og anvendes i alle tilfælde, hvor en bestandsmodel er opsat for en fiskebestand.	Fiskerikontrol med kameraovervågning I forbindelse med forhandlingerne om 2020 fiskekvoterne i Nordsøen, Skagerrak og Kattegat blev det aftalt, at Danmark gennemfører et projekt med elektronisk monitorering i hovedparten af bundtrawlfiskeriet i Kattegat. Det er endnu ikke afklaret, i hvilket omfang videomateriale fra projektet vil blive brugt i relation til biologiske undersøgelser, men vil potentielt kunne bidrage til en bedre vurdering af fiskeri-dødeligheden for nogle fiskearter. Projektet gennemføres for perioden 2020-2022 og en eventuel forlængelse eller udvidelse af projektet er på nuværende tidspunkt uafklaret.	NHAS - North Sea Herring Acoustic Survey Dette survey har til formål, at monitere udbredelsen, bestandsstørrelserne og den årlige rekruttering af sild og brisling i den østlige Nordsø, Skagerrak og Kattegat. NHAS finder sted en gang om året i 2-3. kvartal i juni-juli. Under dette survey anvendes akustik til at aflede akustiske indicer for fiskenes bestandsstørrelser. Desuden anvendes pelagiske trawl til at validere artsammensætningen for de akustiske data og alle fangsterne registreres til art, og yderligere biologiske parametre måles for sild og brisling (længde, alder, køn, seksuel modenhed). NHAS er internationalt koordineret igennem ICES arbejdsgruppen HERSUR og data anvendes af arbejdsgrupperne WGIPS og HAWG til assessment og rådgivning.	IESNS - International Ecosystem Survey in the Nordic Seas Dette survey har til formål, at monitere udbredelsen, bestandsstørrelserne og den årlige rekruttering pelagiske fiskebestande i Norskehavet mellem 62⁰ -74⁰ N, med særlig fokus på målarterne sild og blåhvilling. IESNS finder sted en gang om året i 2. kvartal i maj. Under dette survey anvendes akustik til at aflede akustiske indicier for fiskenes bestandsstørrelser. Desuden anvendes pelagiske trawl til at validere artsammensætningen for de akustiske data og alle fangsterne registreres til art, og yderligere biologiske parametre måles for sild, brisling og makrel (længde, alder, køn, seksuel modenhed). IESNS er internationalt koordineret igennem ICES arbejdsgruppen WGIPS og data anvendes af arbejdsgrupperne WGIPS og HAWG til assessment og rådgivning.	NSSS - North Sea Sandeels Survey Dette survey har til formål, at monitere udbredelsen, bestandsstørrelserne og den årlige rekruttering af tobis i Nordsøen. NSSS finder sted en gang om året i 4. kvartal i november. Under dette survey benyttes et modificeret muslingeskrab, og for stikprøver af de fangede tobis registreres længde, alder, køn, vægt og seksuel modenhed. Desuden indsamles også hydrografiske data med CTD og bundprøver indsamles med Van Veen grab. NSSS er internationalt koordineret igennem ICES arbejdsgruppen NSSKWG og den samme arbejdsgruppe anvender data til assessment og rådgivning.	NTV3&4 - Nephrops TV survey in FU 3 og 4 Dette survey har til formål, at monitere udbredelsen og bestandsstørrelsen af jomfruhummer i Skagerrak og Kattegat. NTV3&4 udføres en gang om året i 2. kvartal i april. Under dette survey benyttes en TV slæde til at videooptage organismerne på havbunden. NTV3&4 er internationalt koordineret igennem ICES arbejdsgruppen WGNSSK og den samme arbejdsgruppe anvender data til assessment og rådgivning.	IESSNS – Coordinated Nordic Seas Ecosystem Survey Dette survey har til formal, at monitere udbredelsen, bestandsstørrelserne og den årlige rekruttering af makrel I Nordsøen. IESSNS finder sted en gang om året i 3. kvartal i juli. Under dette survey benyttes et kommercielt trawl net, og alle fangsterne registreres til art og længde, og yderligere biologiske parametre måles for udvalgte arter sild, brisling og makrel (længde, alder, køn, seksuel modenhed). IESSNS er internationalt koordineret igennem ICES arbejdsgruppen WGIPS og data anvendes af arbejdsgruppen WGWIDE.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The sub-programme provides information on fisheries in EU countries. Data on the fish stock is collected by means of fishing samples and sonars. The aim is to provide information, inter alia, on scientific analysis and advice in support of the Common Fisheries Policy.	The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.	Verslinių žuvų rūšių (menkė, strimelė, brėtlingis ir plekšnė) duomenys renkami pagal Lietuvos nacionalinės žuvininkystės duomenų rinkimo programą. Tyrimai pagal Duomenų rinkimo programą vykdomi 4 kartus per metus. Du kartai dugniniu tralu menkės ir plekšnės rodikliams skaičiuoti ir 2 kartai akustikos tyrimai strimelių ir brėtlingių rodikliams skaičiuoti. D3C1 rodiklio skaičiavimui taip pat renkama biologiniai mėginiai iš verslinių laimikių. Verslinių mėginių rinkimas priklauso nuo žvejybos laiko ir intensyvumą. Verslinių mėginių ėmimas vyksta du kartus per mėnesį kiekvienai verslinei rūšiai, jei vyksta žvejyba. Pagal gautus duomenis, ICES skaičiuoja vertes D3C1 ir D3C2 kriterijų rodikliams (mirtingumo dėl žvejybos koeficientas (F) ir neršiančių išteklių biomasė (SSB) atskiriems Baltijos jūros pakvadračiams. Nacionaliniu lygiu skaičiuojamos vertės D3C3 kriterijaus rodikliams: 1) populiacijos pasiskirstymas pagal amžių ir dydį ir 2) didesnių už vidutinę pirmos lytinės brandos normą žuvų proporcija.	The purpose of the monitoring is to assess the ecological status of Baltic sea including one of significant indicators status of populations of fish species fished for commercial purposes as well as changes in the species distribution, population size and condition, and other characteristics of fish stock state and level of pressure of the fishing activities by using information obtained in the frame of the fisheries data collection programme and monitoring surveys of fish stocks in international hydroacoustic surveillance and other fisheries and ecosystem surveys. The aim is to provide good information on the state of fish stocks. This information is used to support sustainable management of marine resources. Corresponding HELCOM monitoring programme Fish, Fisheries and Shellfish and sub-programme Coastal Fish. In the HELCOM region monitoring of this sub-programme is partly coordinated. The sub-programme is coordinated within HELCOM FISH-PRO II to facilitate comparability of data across areas and harmonized assessments. The evaluation of the stocks of the main industrial species in the Baltic Sea is coordinated by the International Council for the Exploration of the Sea (ICES). The Baltic Sea herring, sprat and cod stocks and flatfish stocks are assessed in the ICES Baltic Fisheries Assessment Working Group (WGBFAS) with the participation of all specialists in the Baltic Sea States and using data from these countries on fish catches and research records. Corresponding working group in the frame of ICES is also ICES Fisheries Resources Steering Group. The requirements for the marine waters of Latvia and the relationship of the specified environmental objectives with the qualitative characteristics characterizing the state of the marine environment are included in Regulation of the Cabinet of Ministers of Republic of Latvia No. 1071 of 23 November 2010, Requirements for the Assessment of the State of the Marine Environment, the Determination of Good Environmental State of the Sea and Development of Marine Environmental Goals. Corresponding legislative acts of the Republic of Latvia concerning fisheries: Fishery Law (adopted 12.04.1995.) and Republic of Latvia Cabinet Regulation No. 296, adopted 2 May 2007 Regulations Regarding Commercial Fishing in Territorial Waters and Economic Zone Waters.	The purpose of the monitoring is to assess the ecological status of Baltic sea including one of core indicators status of populations of fish species (spawning stock biomass) fished for commercial purposes as well as changes in the species distribution, population size and condition, and other characteristics of fish stock state by using information obtained in the frame of the fisheries data collection programme and monitoring surveys of fish stocks in international hydroacoustic surveillance and other fisheries and ecosystem surveys. The aim is to provide good information on the state of fish stocks. This information is used to support sustainable management of marine resources. Corresponding HELCOM monitoring programme Fish, Fisheries and Shellfish and sub-programme Coastal Fish. In the HELCOM region monitoring of this sub-programme is partly coordinated. The sub-programme is coordinated within HELCOM FISH-PRO II to facilitate comparability of data across areas and harmonized assessments. The evaluation of the stocks of the main industrial species in the Baltic Sea is coordinated by the International Council for the Exploration of the Sea (ICES). The Baltic Sea herring, sprat and cod stocks and flatfish stocks are assessed in the ICES Baltic Fisheries Assessment Working Group (WGBFAS), with the participation of all specialists in the Baltic Sea States and using data from these countries on fish catches and research records. Corresponding working group in the frame of ICES is also ICES Fisheries Resources Steering Group. The requirements for the marine waters of Latvia and the relationship of the specified environmental objectives with the qualitative characteristics characterizing the state of the marine environment are included in Regulation of the Cabinet of Ministers of Republic of Latvia No. 1071 of 23 November 2010, Requirements for the Assessment of the State of the Marine Environment, the Determination of Good Environmental State of the Sea and Development of Marine Environmental Goals. Corresponding legislative acts of the Republic of Latvia concerning fisheries: Fishery Law (adopted 12.04.1995.) and Republic of Latvia Cabinet Regulation No. 296, adopted 2 May 2007 Regulations Regarding Commercial Fishing in Territorial Waters and Economic Zone Waters.	The purpose of the monitoring is to assess the ecological status of Baltic sea including one of significant indicators status of populations of fish species (age and size distribution of individuals) fished for commercial purposes as well as changes in the species distribution, population size and condition, and other characteristics of fish stock state by using information obtained in the frame of the fisheries data collection programme and monitoring surveys of fish stocks in international hydroacoustic surveillance and other fisheries and ecosystem surveys. The aim is to provide good information on the state of fish stocks. This information is used to support sustainable management of marine resources. Corresponding HELCOM monitoring programme Fish, Fisheries and Shellfish and sub-programme Coastal Fish. In the HELCOM region monitoring of this sub-programme is partly coordinated. The sub-programme is coordinated within HELCOM FISH-PRO II to facilitate comparability of data across areas and harmonized assessments. The evaluation of the stocks of the main industrial species in the Baltic Sea is coordinated by the International Council for the Exploration of the Sea (ICES). The Baltic Sea herring, sprat and cod stocks and flatfish stocks are assessed in the ICES Baltic Fisheries Assessment Working Group (WGBFAS), with the participation of all specialists in the Baltic Sea States and using data from these countries on fish catches and research records. Corresponding working group in the frame of ICES is also ICES Fisheries Resources Steering Group. The requirements for the marine waters of Latvia and the relationship of the specified environmental objectives with the qualitative characteristics characterizing the state of the marine environment are included in Regulation of the Cabinet of Ministers of Republic of Latvia No. 1071 of 23 November 2010, Requirements for the Assessment of the State of the Marine Environment, the Determination of Good Environmental State of the Sea and Development of Marine Environmental Goals. Corresponding legislative acts of the Republic of Latvia concerning fisheries: Fishery Law (adopted 12.04.1995.) and Republic of Latvia Cabinet Regulation No. 296, adopted 2 May 2007 Regulations Regarding Commercial Fishing in Territorial Waters and Economic Zone Waters.	The ichthyological monitoring of the Polish Exclusive Economic Zone in the deepwater zone of Polish marine area has been carried out as a part of national environmental monitoring since 2011, based on data from BITS (Baltic International Trawl Surveys). BITS consist of cruises of particular Baltic countries being temporally and spatially coordinated by ICES. BITS methodology establishes use of standarized bottom trawl of the same design for scientific catches and use of the same research method for hauling sites sampling, data collection and uploading of collected data to the ICES common database - DATRAS, supplemented with measurement and ichthyological analysis of all fish species (including non-commercial).	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.	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	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	Offshore fish refers to those fish species that live a significant part of their lives in the open sea off the coast, such as herring, sprat and cod. The monitoring of these species and also commercial crustaceans such as crabfish, North Sea shrimp and lobster is coordinated between several countries in the Baltic Sea and the North Sea area, and takes place via acoustic methods and trawl surveys. Data are also collected by sampling on board commercial fishing boats and catches in ports. Several of the species monitored are used in commercial fishing (see programme Commercial fisheries) and all surveys described here are carried out within the framework of the data collection on fish and fisheries governed by EU legislation ((EU) 2017/1004, (EU) 2019 / 909 and (EU) 2019/910). The data collection forms the basis for the scientific basis for the EU Common Fisheries Policy (CFP) and the information is used in the work of the International Council for the Exploration of the Sea (ICES) to produce a basis for the fishing quotas decided by the EU. Data collection is also done for bycatches in the fishery, see programme Bycatch. Trawling of demersal fish in the North Sea (IBTS) started 1972 Trawling of demersal fish in the Baltic Sea (BITS) started 1978 Acoustic survey of pelagic fish (BIAS) started 1978 (Baltic Sea only) Sampling on board commercial fishing boats in the Baltic Sea and Kattegat stareted 1996 Sampling on board commercial fishing boats in the Skagerrak started 2002 Sampling of commercial catches in ports: different starting years for different species Frequency: Trawl surveys are carried out 6-monthly and control of fisheries 3-monthly.	What is currently included in the targeted monitoring is the ten-legged crustacean Nephrops norvegicus. The species is nocturnal and lives on and buried in solid clay bottoms. Along the coast of Sweden, the species occur in the Kattegat and Skagerrak. Nephrops norvegicus is an important commercial species that is fished through bottom trawling. In addition to Nephrops norvegicus, other species that live in the same habitat, such as sea pens and other coral animals, can be injured or die as a result of trawling. The purpose of monitoring Nephrops norvegicus is to map the abundance of the species in areas that are fished. This is done in a UWTV survey (Under Water TV), ie by filming the seabed with an underwater camera and counting the number of inhabited holes per unit area. During the monitoring, the effects of trawling can also be assessed. The geographical coverage of the monitoring is based on the main catchment areas and is thus expected to cover the species main distribution areas. Data collection (in accordance with EU legislation (EU) 2017/1004, (EU) 2019/909 and (EU) 2019/910) through UWTV is coordinated by ICES's working group WGNEPS between several countries in the North Sea area.
Monitoring purpose	Environmental state and impacts Human activities causing the pressures	Environmental state and impacts Human activities causing the pressures	Environmental state and impacts	Environmental state and impacts	Environmental state and impacts	Environmental state and impacts	Environmental state and impacts	Environmental state and impacts	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Human activities causing the pressures Pressures in the marine environment	Human activities causing the pressures Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures	Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	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	Environmental state and impacts	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
Other policies and conventions	Birds Directive Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive		Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Habitats Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)		Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes OSPAR Coordinated Environmental Monitoring Programme	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) OSPAR Coordinated Environmental Monitoring Programme	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes Water Framework Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) HELCOM Monitoring programmes	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	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 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 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
Regional cooperation - coordinating body	Other		Other						Other	Other	Other	Other	Other	Other		Other	OSPAR Other	Other	Other	Other		HELCOM	Other	Other	HELCOM Other		HELCOM	HELCOM	HELCOM	Other	Other	Other	HELCOM Other	Other	HELCOM Other	HELCOM OSPAR	HELCOM Other
Regional cooperation - countries involved									DE DK FR NL SE UK	DE DK EE LT LV PL SE	DK SE								DK SE											DE DK EE FI LT LV PL SE				DE DK FI				DK
Regional cooperation - implementation level	Coordinated data collection		Coordinated data collection						Joint data collection	Joint data collection	Joint data collection	Joint data collection	Common monitoring strategy	Coordinated data collection	Agreed data collection methods	Joint data collection	Joint data collection	Joint data collection	Coordinated data collection	Joint data collection		Coordinated data collection	Agreed data collection methods	Agreed data collection methods	Agreed data collection methods		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	Coordinated data collection
Monitoring details	\|\| MP_86 \|\|	\|\| MP_137 \|\|	\|\| MP_77 \|\| Deutschland nimmt seit 1991 mit FFS Solea zweimal jährlich teil und beprobt die westliche Ostsee mit ungefähr 120 Stationen jährlich (2 mal 20 Tage Reisedauer). Dänemark, Schweden, Estland, Lettland, Litauen, Russland, Polen und Deutschland erheben fast zeitgleich auf ihren Schiffen Daten zur Häufigkeit sowie zu Länge, Gewicht, und ggfs. Geschlecht, Reife und Gesundheitszustand der Nutzfische.	\|\| MP_79 \|\|	\|\| MP_82 \|\| Details zum Monitoring können im Manual nachgelesen werden.	\|\| MP_83 \|\| Während der gesamten Laichzeit, also von Anfang März bis Ende Juni, werden 36 Stationen im Strelasund/Greifswalder Bodden in wöchentlichen Abständen beprobt. Die Heringslarven werden dabei quantitativ mit Plankton-Bongonetzen gefangen.	\|\| MP_85 \|\| Mit einem Schleppnetz (TV3/520 & PSN 388) werden Fischereihols in verschiednen Tiefenstufen durchgeführt. Im Sommer liegt das Hauptuntersuchungsgebiet in der Bornholm See und im Arkona Becken.	\|\| MP_89 \|\|														Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database.		Fishermensâ reporting to authorities.		Data are collected according to the fisheries data collection programme. For the estimation of the fishing mortality analytical assessment of fish stocks for major industrial fish indicator species (herring, sprat, cod and flatfish) is used using data both from the commercial and research fishing surveys. Data about mortality caused by fishing, fishing act parameters and biological samples are obtained in several ways: - from the fishermen, - when experts of Institute of Food Safety, Animal Health and Environment BIOR participate as observers in industrial fishing trips, - during the international surveys. Data on catches of salmon, trout, cod and eel in recreational fisheries also are collected. For the calculation of the fish mortality information about caught fish distribution in the age groups have to be collected using data from biological analysis (weight, age etc.). For collecting of samples in ports and on vessels 2 methods are used: - for coastal fishing according to agreements with BIOR fishermen collect and submit samples of specific species to BIOR; - for fishing in open sea vessel, on which sampling have to be performed, is chosen randomly. Additional biological samples are collected by BIOR specialists participating in industrial fishing trips. For fish species subject to an international stock assessment on the basis of the biological parameters obtained, fish catches are recalculated in quarters and in total per year. 3 kinds of international surveys are used: 1. Baltic Sea international trawling surveys. Aim collect data about the state of cod and flounder stock (bottom trawling) and herring and sprat (pelagic trawling) as well as the size of it addition. Surveys for demersal fish are carried out twice a year - in March, December, for pelagic fish once per year in determined period in standard route crossing the ICES statistical rectangles. During trips fish hydroacoustic records are carried out, oceanographic and ihtioplankton samples are collected. Trawling is done in the light hours of the day. Trawling is done at random on a specified network of stations from the trawl track database. 2. Baltic Sea international hydroacoustic survey in standard route twice per year in May and October, in ICES 28th sub-region and in the N of 26th sub-region, using research pelagic trawl for control trawling. Catches are weighed and sorted by species. 3. Gulf of Riga acoustic herring survey 1 per year together with EMI.	Data are collected according to the fisheries data collection programme. For the estimation of spawning stock biomass analytical assessment of fish stocks for major industrial fish indicator species (herring, sprat, cod and flatfish) is used using data both from the commercial and research fishing surveys. Data about spawning stock biomass, fishing act parameters and biological samples are obtained in several ways: - from the fishermen, - when experts of Institute of Food Safety, Animal Health and Environment BIOR participate as observers in industrial fishing trips, - during the international surveys. For the calculation of the spawning stock biomass information about caught fish distribution in the age groups have to be collected using data from biological analysis (weight, age etc.). For collecting of samples in ports and on vessels 2 methods are used: - for coastal fishing according to agreements with BIOR fishermen collect and submit samples of specific species to BIOR; - for fishing in open sea vessel, on which sampling have to be performed, is chosen randomly. Additional biological samples are collected by BIOR specialists participating in industrial fishing trips. For fish species subject to an international stock assessment on the basis of the biological parameters obtained, fish catches are recalculated in quarters and in total per year. 3 kinds of international surveys are used: 1. Baltic Sea international trawling surveys. Aim collect data about the state of cod and flounder stock (bottom trawling) and herring and sprat (pelagic trawling) as well as the size of it addition. Surveys for demersal fish are carried out twice a year - in March, December, for pelagic fish once per year in determined period in standard route crossing the ICES statistical rectangles. During trips fish hydroacoustic records are carried out, oceanographic and ihtioplankton samples are collected. Trawling is done in the light hours of the day. Trawling is done at random on a specified network of stations from the trawl track database. 2. Baltic Sea international hydroacoustic survey in standard route twice per year in May and October, in ICES 28th sub-region and in the N of 26th sub-region, using research pelagic trawl for control trawling. Catches are weighed and sorted by species. 3. Gulf of Riga acoustic herring survey 1 per year together with EMI.	Data are collected according to the fisheries data collection programme. For the estimation of the age and size distribution of individuals in the populations of commercially-exploited species analytical assessment of fish stocks for major indicator species (herring, sprat, cod and flatfish) is used using data both from the commercial and research fishing surveys. Data about age and size distribution, fishing act parameters and biological samples are obtained: - from the fishermen, - when experts of Institute of Food Safety, Animal Health and Environment BIOR participate as observers in industrial fishing trips, - during the international surveys. Data on catches of salmon, trout, cod and eel in recreational fisheries also are collected. For the calculation of the age and size distribution information about caught fish distribution in the age groups have to be collected (weight, age etc.). Methods used for collecting of samples in ports and on vessels: - for coastal fishing according to agreements with BIOR fishermen collect and submit samples of specific species to BIOR; - for fishing in open sea vessel, on which sampling have to be performed, is chosen randomly. Additional biological samples are collected by BIOR specialists participating in industrial fishing trips. For fish species subject to an international stock assessment on the basis of the biological parameters obtained, fish catches are recalculated in quarters and in total per year. International surveys: 1. Baltic Sea international trawling surveys collecting data about the state of cod and flounder stock (bottom trawling) and herring and sprat (pelagic trawling) as well as the size of it addition. Surveys for demersal fish are carried out twice a year in March, December, for pelagic fish once per year in determined period in standard route crossing the ICES statistical rectangles. During trips fish hydroacoustic records are carried out, oceanographic and ihtioplankton samples are collected. Trawling is done in the light hours of the day. Trawling is done at random on a specified network of stations from the trawl track database. 2. Baltic Sea international hydroacoustic survey in standard route twice per year in May and October, in ICES 28th sub-region and in the N of 26th sub-region, using research pelagic trawl for control trawling. Catches are weighed and sorted by species. 3. Gulf of Riga acoustic herring survey 1 per year together with EMI.
Surface-feeding birds																									Element Surface-feeding birds (grouped) GESCriteria D1C1 P_Parameters Mortality (weight/volume; number of individuals)
Pelagic-feeding birds																									Element Pelagic-feeding birds (grouped) GESCriteria D1C1 P_Parameters Mortality (weight/volume; number of individuals)
Benthic-feeding birds																									Element Benthic-feeding birds (grouped) GESCriteria D1C1 P_Parameters Mortality (weight/volume; number of individuals)
Small toothed cetaceans																									Element Phocoena phocoena GESCriteria D1C1 P_Parameters Mortality (weight/volume; number of individuals)
Seals																									Element Halichoerus grypus Pusa hispida GESCriteria D1C1 P_Parameters Mortality (weight/volume; number of individuals)
Coastal fish	Element Abramis brama Anguilla anguilla Coregonus maraena Platichthys flesus GESCriteria D1C2 D3C1 D3C2 D3C3 P_Parameters Abundance (number of individuals) Other Mortality (weight/volume; number of individuals) Mortality rate Biomass of Spawning Stock (SSB) ParameterOther Rekrutierung von Glas- und Gelbaalen als Index der nicht festgelegt		Element Abramis brama Acipenser oxyrinchus Coregonus maraena Esox lucius Lampetra fluviatilis Leuciscus aspius Platichthys flesus Salmo salar Vimba vimba GESCriteria D1C2 D1C3 D1C4 D3C1 D3C2 D3C3 P_Parameters Abundance (number of individuals) Other Distribution (spatial) Mortality (weight/volume; number of individuals) Mortality rate Biomass of Spawning Stock (SSB) ParameterOther Spezifische Parameter im Zusammenhang mit D1C3 sin Spezifische Parameter im Zusammenhang mit der Verb nicht festgelegt																			Element Abramis brama Alburnus alburnus Alosa fallax Ammodytes tobianus Anguilla anguilla Blicca bjoerkna Carassius carassius Carassius gibelio Cobitis taenia Coregonus maraena Coregonus widegreni Cyprinus carpio Esox lucius Gadus morhua Gobio gobio Gobius niger Gymnocephalus cernua Hyperoplus lanceolatus Lampetra fluviatilis Leuciscus aspius Leuciscus idus Leuciscus leuciscus Lota lota Neogobius melanostomus Osmerus eperlanus Platichthys flesus Platichthys solemdali Rutilus rutilus Sander lucioperca Scardinius erythrophthalmus Scophthalmus maximus [Psetta maxima] Squalius cephalus Tinca tinca Vimba vimba Zoarces viviparus GESCriteria D1C2 D1C3 D1C4 P_Parameters Abundance (number of individuals) Other Biomass Age distribution Length Sex distribution Distribution (spatial) ParameterOther Abundance index of European eel in monitoring catc Mass (catch mass per unit effort) Mass (catch weight per unit effort)					Element Gadus morhua GESCriteria D3C1 P_Parameters Mortality (weight/volume; number of individuals) Other ParameterOther Number of individuals in age groups	Element Gadus morhua GESCriteria NotRelevan P_Parameters Biomass of Spawning Stock (SSB) ParameterOther Number of individuals in age groups	Element Gadus morhua GESCriteria NotRelevan P_Parameters Age distribution Size distribution ParameterOther Number of individuals in age groups				Element Anguilla anguilla GESCriteria D1C2 D1C4 P_Parameters Abundance (number of individuals) Biomass Other Distribution (range) ParameterOther Length Mass Age distribution Lifestage Stage of ma			Element 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 GESCriteria D1C2 D1C3 D1C4 P_Parameters Abundance (number of individuals) Biomass Age distribution Other Sex distribution Distribution (range) Distribution (spatial) ParameterOther Developmental state of gonads Presence of parasite
Pelagic shelf fish	Element Belone belone Clupea harengus Sprattus sprattus GESCriteria D1C2 D3C1 D3C2 D3C3 P_Parameters Abundance (number of individuals) Mortality (weight/volume; number of individuals) Mortality rate Other Biomass of Spawning Stock (SSB) ParameterOther nicht festgelegt		Element Alosa fallax Belone belone Clupea harengus Cyclopterus lumpus Salmo trutta trutta Sprattus sprattus GESCriteria D1C2 D3C1 D3C2 D3C3 P_Parameters Abundance (number of individuals) Mortality (weight/volume; number of individuals) Mortality rate Other Biomass of Spawning Stock (SSB) ParameterOther nicht festgelegt	Element Alosa fallax Clupea harengus Sprattus sprattus GESCriteria D1C2 D3C1 D3C2 D3C3 P_Parameters Abundance (number of individuals) Mortality (weight/volume; number of individuals) Mortality rate Biomass of Spawning Stock (SSB) Other ParameterOther nicht festgelegt	Element Alosa fallax Clupea harengus Sprattus sprattus GESCriteria D1C2 D3C1 D3C2 D3C3 P_Parameters Abundance (number of individuals) Mortality (weight/volume; number of individuals) Mortality rate Biomass of Spawning Stock (SSB) Other ParameterOther nicht festgelegt	Element Clupea harengus GESCriteria D1C3 P_Parameters Other ParameterOther relative Abundanz der Heringslarven		Element Salmo trutta trutta GESCriteria D1C2 P_Parameters Abundance (number of individuals)														Element Belone belone Clupea harengus Coregonus albula Coregonus lavaretus Cyclopterus lumpus Pelecus cultratus Salmo salar Salmo trutta trutta Sprattus sprattus GESCriteria D1C2 D1C3 D1C4 P_Parameters Abundance (number of individuals) Other Age distribution Length Sex distribution Distribution (spatial) ParameterOther Mass (catch mass per unit effort) Mass (catch weight per unit effort)	Element Clupea harengus Sprattus sprattus GESCriteria D1C1 D1C2 D1C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass Age distribution	Element Salmo trutta trutta GESCriteria D1C2 P_Parameters Other ParameterOther Number of spawning individuals; Number of smolts			Element Clupea harengus Sprattus sprattus GESCriteria D3C1 P_Parameters Mortality (weight/volume; number of individuals) Other ParameterOther Number of individuals in age groups	Element Clupea harengus Sprattus sprattus GESCriteria NotRelevan P_Parameters Biomass of Spawning Stock (SSB) ParameterOther Number of individuals in age groups	Element Clupea harengus Sprattus sprattus GESCriteria NotRelevan P_Parameters Age distribution Size distribution ParameterOther Number of individuals in age groups						Element Salmo salar Salmo trutta trutta GESCriteria D1C2 D1C4 P_Parameters Abundance (number of individuals) Biomass Other Distribution (range) ParameterOther Age distribution Lifestage Presence of parasites (		Element Clupea harengus Cyclopterus lumpus Dicentrarchus labrax Scomber scombrus Sprattus sprattus Squalus acanthias GESCriteria D1C2 D1C3 D1C4 P_Parameters Abundance (number of individuals) Biomass Age distribution Length Other Sex distribution Distribution (range) ParameterOther Mass Size distribution Developmental state of gona
Demersal shelf fish	Element Gadus morhua Limanda limanda Pleuronectes platessa GESCriteria D1C2 D1C3 D1C4 D3C1 D3C2 D3C3 P_Parameters Other Mortality (weight/volume; number of individuals) Mortality rate Biomass of Spawning Stock (SSB) ParameterOther Spawning Stock Biomass Spezifische Parameter im Zusammenhang mit D1C3 sin Spezifische Parameter im Zusammenhang mit der Verb nicht festgelegt		Element Enchelyopus cimbrius Gadus morhua Limanda limanda Lumpenus lampretaeformis Pleuronectes platessa Scophthalmus rhombus Trachinus draco GESCriteria D1C2 D1C3 D1C4 D3C1 D3C2 D3C3 P_Parameters Abundance (number of individuals) Other Mortality (weight/volume; number of individuals) Mortality rate Biomass of Spawning Stock (SSB) ParameterOther Spezifische Parameter im Zusammenhang mit D1C3 sin Spezifische Parameter im Zusammenhang mit der Verb nicht festgelegt																			Element Cottus gobio Myoxocephalus quadricornis Myoxocephalus scorpius Perca fluviatilis Taurulus bubalis GESCriteria D1C2 D1C3 D1C4 P_Parameters Abundance (number of individuals) Other Biomass Age distribution Length Sex distribution Distribution (spatial) ParameterOther Mass (catch mass per unit effort) Mass (catch weight per unit effort)					Element Limanda limanda Platichthys flesus Pleuronectes platessa GESCriteria D3C1 P_Parameters Mortality (weight/volume; number of individuals) Other ParameterOther Number of individuals in age groups	Element Limanda limanda Platichthys flesus Pleuronectes platessa GESCriteria NotRelevan P_Parameters Biomass of Spawning Stock (SSB) ParameterOther Number of individuals in age groups	Element Limanda limanda Platichthys flesus Pleuronectes platessa GESCriteria NotRelevan P_Parameters Age distribution Size distribution ParameterOther Number of individuals in age groups	Element Gadus morhua Merlangius merlangus Platichthys flesus Pleuronectes platessa GESCriteria D1C3 P_Parameters Length Other ParameterOther biomass							Element 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 GESCriteria D1C2 D1C3 D1C4 P_Parameters Abundance (number of individuals) Biomass Age distribution Length Other Sex distribution Distribution (range) ParameterOther Mass Size distribution Developmental state of gona
Commercially exploited fish and shellfish	Element Scophthalmus maximus [Psetta maxima] Scophthalmus rhombus GESCriteria D1C3 D1C4 D3C1 D3C2 D3C3 P_Parameters Other Mortality (weight/volume; number of individuals) Mortality rate Biomass of Spawning Stock (SSB) ParameterOther Spezifische Parameter im Zusammenhang mit D1C3 sin Spezifische Parameter im Zusammenhang mit der Verb nicht festgelegt	Element Gadus morhua GESCriteria D1C2 D3C1 P_Parameters Abundance (number of individuals) Length Mortality rate	Element Scophthalmus maximus [Psetta maxima] GESCriteria D1C3 D1C4 D3C1 D3C2 D3C3 P_Parameters Other Mortality (weight/volume; number of individuals) Mortality rate Biomass of Spawning Stock (SSB) ParameterOther Spezifische Parameter im Zusammenhang mit D1C3 sin Spezifische Parameter im Zusammenhang mit der Verb nicht festgelegt				Element Gadus morhua GESCriteria D3C2 P_Parameters Biomass of Spawning Stock (SSB)		Element Aequipecten opercularis Amblyraja radiata Anarhichas lupus Argentina silus Argentinidae Brosme brosme Callista chione Cancer pagurus Capros aper Chelidonichthys cuculus Chelidonichthys lucerna Clupea harengus Crystallogobius linearis Eledone cirrhosa Engraulis encrasicolus Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Gymnammodytes semisquamatus Helicolenus dactylopterus Hippoglossoides platessoides Homarus gammarus Illex coindetii Labrus bergylta Lepidorhombus whiffiagonis Leucoraja naevus Limanda limanda Loligo forbesii Loligo vulgaris Lophius budegassa Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Microchirus spp. Micromesistius poutassou Microstomus kitt Mullus surmuletus Mustelus spp. Nephrops norvegicus Phycis blennoides Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja brachyura Raja clavata Raja montagui Sardina pilchardus Scomber scombrus Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Sepia officinalis Solea solea Sprattus sprattus Squalus acanthias Trachurus trachurus Trisopterus esmarkii Trisopterus luscus Trisopterus minutus Zeus faber GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Size distribution Other ParameterOther Otolith/age Sexual maturity	Element Ammodytes spp. Anarhichas lupus Anguilla anguilla Belone belone Cancer pagurus Carcinus maenas Chelon labrosus Clupea harengus Ctenolabrus rupestris Dicentrarchus labrax Engraulis encrasicolus Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Hippoglossoides platessoides Homarus gammarus Labrus bergylta Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Microstomus kitt Mullus surmuletus Nephrops norvegicus Perca fluviatilis Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja clavata Sander lucioperca Sardina pilchardus Scomber scombrus Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea Sprattus sprattus Squalus acanthias Symphodus melops Trisopterus esmarkii Trisopterus luscus Trisopterus minutus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Size distribution Other ParameterOther Age Age/otolith	Element Ammodytes spp. Anarhichas lupus Anguilla anguilla Belone belone Cancer pagurus Carcinus maenas Chelon labrosus Clupea harengus Ctenolabrus rupestris Dicentrarchus labrax Engraulis encrasicolus Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Hippoglossoides platessoides Homarus gammarus Labrus bergylta Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Microstomus kitt Mullus surmuletus Nephrops norvegicus Perca fluviatilis Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja clavata Sander lucioperca Sardina pilchardus Scomber scombrus Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea Sprattus sprattus Squalus acanthias Symphodus melops Trisopterus esmarkii Trisopterus luscus Trisopterus minutus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Size distribution Other ParameterOther Age Age/otolith	Element Ammodytes spp. Anarhichas lupus Anguilla anguilla Belone belone Cancer pagurus Carcinus maenas Chelon labrosus Clupea harengus Ctenolabrus rupestris Dicentrarchus labrax Engraulis encrasicolus Eutrigla gurnardus Gadus morhua Glyptocephalus cynoglossus Hippoglossoides platessoides Homarus gammarus Labrus bergylta Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Microstomus kitt Mullus surmuletus Nephrops norvegicus Perca fluviatilis Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Raja clavata Sander lucioperca Sardina pilchardus Scomber scombrus Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea Sprattus sprattus Squalus acanthias Symphodus melops Trisopterus esmarkii Trisopterus luscus Trisopterus minutus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Size distribution Other ParameterOther Age Age/otolith	Element Aequipecten opercularis Alopias spp. Amblyraja radiata Ammodytes spp. Anarhichas lupus Anguilla anguilla Argentina silus Belone belone Brosme brosme Buccinum undatum Cancer pagurus Capros aper Carcinus maenas Chelidonichthys cuculus Chelidonichthys lucerna Chelon labrosus Clupea harengus Conger conger Crangon crangon Crystallogobius linearis Ctenolabrus rupestris Dicentrarchus labrax Dipturus batis Eledone cirrhosa Engraulis encrasicolus Eutrigla gurnardus Gadus morhua Galeorhinus galeus Glyptocephalus cynoglossus Gymnammodytes semisquamatus Helicolenus dactylopterus Hippoglossoides platessoides Homarus gammarus Illex coindetii Labrus bergylta Lamna nasus Lepidorhombus whiffiagonis Leucoraja naevus Limanda limanda Loligo forbesii Loligo vulgaris Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Microchirus spp. Micromesistius poutassou Microstomus kitt Molva dypterygia Molva molva Mullus surmuletus Mustelus spp. Nephrops norvegicus Octopodidae Pandalus borealis Perca fluviatilis Phycis blennoides Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Prionace glauca Raja brachyura Raja clavata Raja montagui Salmo salar Sander lucioperca Sarda sarda Sardina pilchardus Scomber japonicus Scomber scombrus Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Sepia officinalis Solea solea Sprattus sprattus Squalus acanthias Symphodus melops Todarodes sagittatus Trachurus trachurus Trisopterus esmarkii Trisopterus luscus Trisopterus minutus Xiphias gladius Zeus faber GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality (weight/volume; number of individuals) Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Size distribution	Element Aequipecten opercularis Alopias spp. Amblyraja radiata Ammodytes spp. Anarhichas lupus Anguilla anguilla Argentina silus Belone belone Brosme brosme Buccinum undatum Cancer pagurus Capros aper Chelidonichthys lucerna Chelon labrosus Clupea harengus Conger conger Crangon crangon Crystallogobius linearis Ctenolabrus rupestris Dicentrarchus labrax Dipturus batis Engraulis encrasicolus Eutrigla gurnardus Gadus morhua Galeorhinus galeus Glyptocephalus cynoglossus Hippoglossoides platessoides Homarus gammarus Labrus bergylta Lamna nasus Lepidorhombus whiffiagonis Leucoraja naevus Limanda limanda Lophius piscatorius Melanogrammus aeglefinus Merlangius merlangus Merluccius merluccius Microchirus spp. Micromesistius poutassou Microstomus kitt Molva molva Mullus surmuletus Mustelus spp. Mytilus edulis Nephrops norvegicus Octopodidae Pandalus borealis Perca fluviatilis Phycis blennoides Platichthys flesus Pleuronectes platessa Pollachius pollachius Pollachius virens Prionace glauca Raja clavata Raja montagui Salmo salar Sander lucioperca Sarda sarda Sardina pilchardus Scomber japonicus Scomber scombrus Scophthalmus maximus Scophthalmus rhombus Scyliorhinus canicula Solea solea Sprattus sprattus Squalus acanthias Todarodes sagittatus Trachurus trachurus Trisopterus esmarkii Trisopterus luscus Xiphias gladius Zeus faber GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality (weight/volume; number of individuals) Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Size distribution	Element Gadus morhua GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality (weight/volume; number of individuals) Abundance (number of individuals) Length	Element Clupea harengus Sprattus sprattus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Other Size distribution ParameterOther Age structure	Element Clupea harengus Micromesistius poutassou Scomber scombrus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Other Size distribution ParameterOther Age structure	Element Ammodytes spp. GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Other Size distribution ParameterOther Age	Element Nephrops norvegicus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Size distribution	Element Clupea harengus Scomber scombrus Sprattus sprattus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Other Size distribution ParameterOther Age Seksuel modenhed		Element Clupea harengus Perca fluviatilis Platichthys flesus Platichthys solemdali Salmo salar Sander lucioperca GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Other Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length ParameterOther Age distribution Age distribution; Sex distribution Mass (commercial catch weight per unit effort) Ratio between annual commercial catch and biomass Sex distribution; Age distribution	Element Clupea harengus Sprattus sprattus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Abundance (number of individuals) Biomass of Spawning Stock (SSB) Other ParameterOther Age distribution	Element Anguilla anguilla Clupea harengus Coregonus lavaretus Gadus morhua Perca fluviatilis Salmo salar Sander lucioperca Sprattus sprattus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality (weight/volume; number of individuals) Abundance (number of individuals) Other Length Size distribution ParameterOther Age Number of spawning individuals; Number of smolts age	Element Esox spp. Perca fluviatilis Sander lucioperca GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality (weight/volume; number of individuals) Biomass of Spawning Stock (SSB) Size distribution ParameterOther age	Element Clupea harengus Gadus morhua Platichthys flesus Sprattus sprattus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Biomass of Spawning Stock (SSB) Length Size distribution				Element Clupea harengus Gadus morhua Platichthys flesus Sprattus sprattus GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality rate Other Biomass of Spawning Stock (SSB) Length Size distribution ParameterOther catches divided by stock size index stock size index from survey						Element 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 GESCriteria D3C2 D3C3 P_Parameters Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Other Size distribution ParameterOther Mass	Element 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 GESCriteria D3C1 D3C2 D3C3 P_Parameters Mortality (weight/volume; number of individuals) Abundance (number of individuals) Biomass of Spawning Stock (SSB) Length Size distribution	Element Nephrops norvegicus GESCriteria D3C2 D3C3 P_Parameters Abundance (number of individuals) Other Size distribution ParameterOther Age distribution Sex distribution
Benthic broad habitats																																						Element Circalittoral mud Offshore circalittoral mud GESCriteria D6C5 P_Parameters Extent Other ParameterOther Abundance (number of individuals) Size distributio
Coastal ecosystems																						Element Fish community GESCriteria D4C1 D4C2 P_Parameters Other Abundance (number of individuals) ParameterOther Abundance of coastal fish key functional groups (C Species composition; Trophic level class of fish s			Element Fish community GESCriteria D4C1 D4C2 P_Parameters Other Abundance (number of individuals) ParameterOther Abundance of Cyprinidae											Element Fish community GESCriteria D4C1 D4C2 D4C3 P_Parameters Other Abundance (number of individuals) Biomass Size distribution ParameterOther Species composition		Element Sub-apex demersal predators GESCriteria D4C2 D4C3 P_Parameters Abundance (number of individuals) Other Size distribution ParameterOther Age distribution Sex distribution
Shelf ecosystems																														Element Fish community GESCriteria D4C3 P_Parameters Size distribution							Element Fish community GESCriteria D4C1 D4C2 D4C3 P_Parameters Other Abundance (number of individuals) Biomass Size distribution ParameterOther Species composition	Element Sub-apex demersal predators GESCriteria D4C2 D4C3 P_Parameters Abundance (number of individuals) Other Size distribution ParameterOther Age distribution Sex distribution
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)																																Element Not Applicable GESCriteria D3C1 P_Parameters Mortality (weight/volume; number of individuals)		Element Not Applicable GESCriteria D3C1 P_Parameters Mortality (weight/volume; number of individuals) Other ParameterOther Species composition, Size distribution, and Inform
Input of nutrients – diffuse sources, point sources, atmospheric deposition																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Pollution load (tonnes/year) - N, P, BHT5
Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) – diffuse sources, point sources, atmospheric deposition, acute events																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Pollution load (tonnes/year) - Hg, Cd, Cu, Pb, Zn,
Input of litter (solid waste matter, including micro-sized litter)																					Element Not Applicable GESCriteria NotRelevan P_Parameters AMO-WC Amount on coastline Amount on seabed Other ParameterOther Amount in sediments; Litter type and material
Input of anthropogenic sound (impulsive, continuous)																					Element Not Applicable GESCriteria NotRelevan P_Parameters Level of sound Other ParameterOther Number of disturbance days - Impulsive underwater
Established non-indigenous species																														Element Neogobius melanostomus GESCriteria D2C2 P_Parameters Abundance (number of individuals)
Coastal defence and flood protection																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Length of defence structure; Coastline pressure in
Offshore structures (other than for oil/gas/renewables)																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Area of structure; Area pressure index
Extraction of minerals (rock, metal ores, gravel, sand, shell)																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Mining volume; Mining area; Area pressure index
Extraction of oil and gas, including infrastructure																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Pipe length (area); Area pressure index
Extraction of water																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Volume
Renewable energy generation (wind, wave and tidal power), including infrastructure																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Area; Area pressure index
Transmission of electricity and communications (cables)																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Cable length (area); Area pressure index
Fish and shellfish harvesting (professional, recreational)																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Catch; By-catch				Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Fishing effort (days)		Element Not Applicable GESCriteria D3C1 P_Parameters Mortality (weight/volume; number of individuals) Other ParameterOther Number of individuals in age groups	Element Not Applicable GESCriteria D3C2 P_Parameters Biomass of Spawning Stock (SSB) ParameterOther Number of individuals in age groups	Element Not Applicable GESCriteria D3C3 P_Parameters Length Other Size distribution ParameterOther Age distribution					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Information regarding the fisherman, fishing metho
Marine plant harvesting																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Amount (kg); Area
Hunting and collecting for other purposes																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Number of individuals hunted by species (waterbird
Aquaculture – marine, including infrastructure																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Production (tonnes); Area; Nutrient load
Transport infrastructure																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Area; Volume (goods and passengers); Number of loa
Transport – shipping																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Number of ships (incl. number of ships complying w
Waste treatment and disposal																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Areas of dumping sites and volume of dumped materi
Tourism and leisure infrastructure																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Number of marinas per coastline; Length of beach
Tourism and leisure activities																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Number of vacationists; Number of visits; People's
Military operations (subject to Article 2(2))																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Number of explosions; Number of trainings; Trainin
Research, survey and educational activities																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Volume of costs on marine researches; Number of re
Restructuring of seabed morphology, including dredging and depositing of materials																					Element Not Applicable GESCriteria NotRelevan P_Parameters Other ParameterOther Soil volume; Extent; Area pressure index
Species affected by incidental by-catch																															Element Not Applicable GESCriteria D1C1 P_Parameters Mortality (weight/volume; number of individuals)
Spatial scope	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD)	Beyond MS Marine Waters EEZ (or similar) Territorial waters	Beyond MS Marine Waters EEZ (or similar) Territorial waters	Beyond MS Marine Waters EEZ (or similar)	Coastal waters (WFD) Territorial waters Transitional waters (WFD)	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	EEZ (or similar)	EEZ (or similar)	EEZ (or similar)	EEZ (or similar)	EEZ (or similar)	EEZ (or similar)	EEZ (or similar)	EEZ (or similar)	Continental shelf (beyond EEZ) EEZ (or similar)	EEZ (or similar)	EEZ (or similar)	EEZ (or similar)	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	EEZ (or similar) Territorial waters	EEZ (or similar)	EEZ (or similar)	EEZ (or similar) Territorial waters	Beyond MS Marine Waters EEZ (or similar) Territorial waters	Beyond MS Marine Waters EEZ (or similar) Territorial waters	Beyond MS Marine Waters EEZ (or similar) Territorial waters	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) EEZ (or similar) Territorial waters	Coastal waters (WFD)	Coastal waters (WFD)	Beyond MS Marine Waters Coastal waters (WFD) EEZ (or similar) Territorial waters	Beyond MS Marine Waters EEZ (or similar) Territorial waters
Marine reporting units	BALDE_MS	BALDE_EEZ	BALDE_MS	BALDE_MS	BALDE_MS	DE_CW_DEMV_WP_13	BALDE_MS	BALDE_FA_3c22 BALDE_FA_3d24	ANS-DK-KA ANS-DK-L2.2.5 ANS-DK-TOTAL ANS-DK-TOTAL-WO_coast DK-TOTAL-part-ANS	ANS-DK-L2.2.1 BAL-DK-BB BAL-DK-BS BAL-DK-HELCOM-KATTEGAT BAL-DK-HELCOM-OSTERSO BAL-DK-HELCOM-STRAITS BAL-DK-HELCOM-TOTAL BAL-DK-SEA_001 BAL-DK-SEA_002 BAL-DK-SEA_003 BAL-DK-SEA_004 BAL-DK-SEA_007 BAL-DK-SEA_05 BAL-DK-SEA_06 BAL-DK-SEA_07 BAL-DK-SEA_09 BAL-DK-TOTAL BAL-DK-TOTAL-WO_coast DK-BAL-EAST-ICES DK-BAL-WEST-ICES DK-TOTAL-part-BAL	ANS-DK-L2.2.1 BAL-DK-HELCOM-KATTEGAT BAL-DK-SEA_001 BAL-DK-SEA_07	ANS-DK-L2.2.1 ANS-DK-L2.2.7 BAL-DK-HELCOM-KATTEGAT BAL-DK-SEA_07	ANS-DK-KA ANS-DK-L2.2.1 ANS-DK-L2.2.5 ANS-DK-L2.2.7 ANS-DK-OSPAR-TOTAL ANS-DK-TOTAL ANS-DK-TOTAL-WO_coast BAL-DK-BB BAL-DK-BS BAL-DK-HELCOM-KATTEGAT BAL-DK-HELCOM-OSTERSO BAL-DK-HELCOM-STRAITS BAL-DK-HELCOM-TOTAL BAL-DK-SEA_001 BAL-DK-SEA_002 BAL-DK-SEA_003 BAL-DK-SEA_004 BAL-DK-SEA_005 BAL-DK-SEA_006 BAL-DK-SEA_007 BAL-DK-SEA_05 BAL-DK-SEA_06 BAL-DK-SEA_07 BAL-DK-SEA_09 BAL-DK-TOTAL BAL-DK-TOTAL-WO_coast DK-ANS-ICES DK-BAL-EAST-ICES DK-BAL-WEST-ICES DK-TOTAL-WO_coast DK-TOTAL-part-ANS DK-TOTAL-part-BAL	ANS-DK-KA ANS-DK-L2.2.1 ANS-DK-L2.2.5 ANS-DK-L2.2.7 ANS-DK-OSPAR-TOTAL ANS-DK-TOTAL BAL-DK-BB BAL-DK-BS BAL-DK-HELCOM-KATTEGAT BAL-DK-HELCOM-OSTERSO BAL-DK-HELCOM-STRAITS BAL-DK-HELCOM-TOTAL BAL-DK-SEA_001 BAL-DK-SEA_002 BAL-DK-SEA_003 BAL-DK-SEA_004 BAL-DK-SEA_005 BAL-DK-SEA_006 BAL-DK-SEA_007 BAL-DK-SEA_05 BAL-DK-SEA_06 BAL-DK-SEA_07 BAL-DK-SEA_09 BAL-DK-TOTAL DK-BAL-WEST-ICES DK-TOTAL DK-TOTAL-WO_coast DK-TOTAL-part-ANS DK-TOTAL-part-BAL	ANS-DK-L2.2.1 BAL-DK-HELCOM-KATTEGAT BAL-DK-SEA_001 BAL-DK-SEA_07	ANS-DK-KA ANS-DK-L2.2.1 ANS-DK-L2.2.5 ANS-DK-L2.2.7 ANS-DK-OSPAR-TOTAL ANS-DK-TOTAL ANS-DK-WO-KA BAL-DK-SEA_001 BAL-DK-SEA_07	ANS-DK-L2.2.5 ANS-DK-TOTAL ANS-DK-TOTAL-WO_coast DK-TOTAL-part-ANS	ANS-DK-KA ANS-DK-L2.2.5 ANS-DK-TOTAL ANS-DK-TOTAL-WO_coast DK-TOTAL-part-ANS	ANS-DK-L2.2.1 ANS-DK-L2.2.7 BAL-DK-SEA_001 BAL-DK-SEA_001-WO_coast BAL-DK-SEA_07	ANS-DK-INNER ANS-DK-L2.2.5 ANS-DK-OUTER ANS-DK-TOTAL-WO_coast DK-TOTAL-part-ANS	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GF-EE-ICES_SD_32 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-NBP	BAL-FI-AS BAL-FI-BB BAL-FI-BS BAL-FI-GF BAL-FI-NB BAL-FI-QK	BAL-FI-AS BAL-FI-BB BAL-FI-BS BAL-FI-GF BAL-FI-NB BAL-FI-QK	BAL-LT-AA-03	BAL-LV-AAA-007 BAL-LV-AAA-009	BAL-LV-AAA-007 BAL-LV-AAA-009	BAL-LV-AAA-007 BAL-LV-AAA-009	BAL-POL-ICHTYO-01	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-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_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_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
Temporal scope (start date - end date)	2002-9999	2002-9999	1981-9999	1978-9999	1999-9999	1977-9999	1992-9999	2002-9999	1983-9999	1988-9999	2008-9999	2004-9999	1995-9999	1983-9999	2020-2022	2007-9999	2004-9999	2003-9999	2011-9999	2018-9999	2015-9999	1975-9999	1992-9999	2002-9999	1980-9999	2005-9999	2021-2026	2021-2026	2021-2026	2011-9999	1996-9999	1994-9999	1969-9999	1973-9999	2004-9999	1960-9999	1972-9999	2011-9999
Monitoring frequency	Weekly	Continually	6-monthly	Yearly	Yearly	Weekly	Yearly	6-monthly	6-monthly	6-monthly	Yearly	Yearly	Continually	Continually	Continually	Yearly	Yearly	Yearly	Yearly	Yearly	Other	Yearly	Yearly	Yearly	Continually	Other	Other	Other	Other	6-monthly	3-monthly	Continually	Yearly	Other	Yearly	Yearly	Other	Yearly
Monitoring type	In-situ sampling coastal In-situ sampling offshore	Other	In-situ sampling coastal In-situ sampling offshore	In-situ sampling coastal In-situ sampling offshore	In-situ sampling land/beach In-situ sampling offshore Other	In-situ sampling coastal	In-situ sampling coastal In-situ sampling offshore	Other	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	Administrative data collection In-situ sampling land/beach In-situ sampling offshore Remote surveillance	Remote surveillance	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	Administrative data collection	In-situ sampling coastal In-situ sampling offshore	In-situ sampling offshore	Administrative data collection In-situ sampling coastal In-situ sampling offshore	Administrative data collection	In-situ sampling offshore Remote surveillance	Administrative data collection In-situ sampling coastal In-situ sampling offshore	Administrative data collection In-situ sampling coastal In-situ sampling offshore	Administrative data collection In-situ sampling coastal In-situ sampling offshore	In-situ sampling offshore	Other Visual observation	Administrative data collection Other	In-situ sampling coastal	Administrative data collection In-situ sampling coastal Visual observation	Administrative data collection In-situ sampling coastal Remote surveillance	In-situ sampling coastal	In-situ sampling offshore	Visual observation
Monitoring method	Other monitoring method	Other monitoring method	SISP 7 - BITS Manual for the Baltic International Trawl Surveys	SISP 8 - IBAS Manual for the International Baltic Acoustic Surveys	SISP 8 - IBAS Manual for the International Baltic Acoustic Surveys	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region 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 HELCOM Manual for monitoring in COMBINE programme SISP 7 - BITS Manual for the Baltic International Trawl Surveys SISP 8 - IBAS Manual for the International Baltic Acoustic Surveys	HELCOM Guidelines for coastal fish monitoring HELCOM Manual for monitoring in COMBINE programme SISP 7 - BITS Manual for the Baltic International Trawl Surveys SISP 8 - IBAS Manual for the International Baltic Acoustic Surveys	HELCOM Guidelines for coastal fish monitoring HELCOM Manual for monitoring in COMBINE programme SISP 7 - BITS Manual for the Baltic International Trawl Surveys SISP 8 - IBAS Manual for the International Baltic Acoustic Surveys	SISP 7 - BITS Manual for the Baltic International Trawl Surveys	Other monitoring method	NEAFC: Recording of Catch and Fishing Effort Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	Other monitoring method	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
Monitoring method other	\|\| MP_086 \|\| Es werden sowohl die aktive Fischerei (Schlepper) als auch die passive Fischerei (Stellnetzkutter, Langleinen, Fischfallen) beprobt. An Bord der Fischereifahrzeuge werden die Rückwurfraten sowie Längenverteilungen in den Anlandungen und Rückwürfen erfasst. Einzelne Fische werden eingehender untersucht und Informationen zu wichtigen biologischen Parametern wie Gewicht, Geschlecht, Reifegrad oder Alter dokumentiert.	\|\| MP_137 \|\| Es werdenganzjährig Proben an Stränden und Häfen genommen sowie Angler befragt An Bord von Angelkuttern wird die Länge von Fischen gemessen. Tagebuchstudien ermöglichen eine kontinuierlich Datenerhebung zu bestimmten Verhaltensweisen (Fang, Ausgaben, etc.), zudem dienen telefonische Befragungen dazu bevölkerungsrepräsentative Studien durchzuführen.	\|\| MP_077 \|\|	\|\| MP_079 \|\|	\|\| MP_082 \|\|	\|\| MP_083 \|\| Erfassung von Herings-Larven	\|\| MP_085 \|\| Fischerei-Standard-Hols mit einem Grundschleppnetz (TV 3/520) und pelagischen Schleppnetz (PSN 388).	\|\| MP_089 \|\| Elektrobefischung, Parr-Habitat-Index, Trout-Habitat-Score	http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP%2010%20-%20Manual%20for%20the%20International%20Bottom%20Trawl%20Surveys%20-%20Revision%20IX.pdf https://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP%202%20MIK2.pdf	http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20%28SISP%29/SISP%207%20-%20Manual%20for%20the%20Baltic%20International%20Trawl%20Surveys%20%28BITS%29.pdf	Link to particular guideline/protocols is not available, but can be accessed on request to DTU Aqua. https://www.aqua.dtu.dk/.	Link to particular guideline/protocols is not available, but can be accessed on request to DTU Aqua. https://www.aqua.dtu.dk/.	Link to particular guideline/protocols is not available, but can be accessed on request to DTU Aqua. https://www.aqua.dtu.dk/.	Er beskrevet i Fiskerikontrollens årsrapporter og på Fiskeristyrelsens hjemmeside. https://fiskeristyrelsen.dk/	Link to particular guideline/protocols is not available, but can be accessed on request to DTU Aqua or the Danish Fisheries Agency. https://www.aqua.dtu.dk/. https://fiskeristyrelsen.dk/	http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP%20 9%20Manual%20for%20International%20Pelagic%20Surveys%20(IPS).pdf	http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP%209%20Manual%20for%20International%20Pelagic%20Surveys%20(IPS).pdf	Link to particular guideline/protocols is not available, but can be accessed on request to DTU Aqua. https://www.aqua.dtu.dk/.	http://www.ices.dk/sites/pub/Publication%20Reports/Expert%20Group%20Report/EOSG/2018/WGNEPS/WGNEPS%20report%202018.pdf	http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP%209%20Manual%20for%20International%20Pelagic%20Surveys%20(IPS).pdf	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	ICES WGBFAS	The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined.	Data collection and handling is coordinated in RCB Baltic group and ICES working groups WGBIFS and WGBAST	Monitoring - https://stat.luke.fi/en/commercial-marine-fishery	ICES. 2017. Manual for the Baltic International Trawl Surveys (BITS). Series of ICES Survey Protocols SISP 7 - BITS. 95 pp. http://doi.org/10.17895/ices.pub.2883; ICES. 2017. Manual for the International Baltic Acoustic Surveys (IBAS). Series of ICES Survey Protocols SISP 8 - IBAS. 47 pp. http://doi.org/10.17895/ices.pub.3368					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 "	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.	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/en/eu-and-international/international-cooperation/data-collection-framework-dcf/efforts-in-sweden.html	https://www.ices.dk/sites/pub/Publication%20Reports/Cooperative%20Research%20Report%20(CRR)/CRR340.pdf
Quality control	\|\| MP_086 \|\| National finden institutseigene Kontrollen statt.	\|\| MP_137 \|\| Institutseigene Kontrollen und Guidelines der ICES WGRFS	\|\| MP_077 \|\| National finden institutseigene Kontrollen statt.	\|\| MP_079 \|\| Planung, Durchführung und Berechnung der Bestandindizes durch die ICES-Arbeitsgruppe ‚Baltic International Fish Survey Working Group (WGBIFS)	\|\| MP_082 \|\| Planung, Durchführung und Berechnung der Bestandindizes durch die ICES-Arbeitsgruppe ‚Baltic International Fish Survey Working Group (WGBIFS)	\|\| MP_083 \|\| National finden institutseigene Kontrollen statt.	\|\| MP_085 \|\| National finden institutseigene Kontrollen statt.	\|\| MP_089 \|\| Verwendung des Parr-Habitat-Index und des Trout-Habitat-Score.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	Fiskeristyrelsen er hovedansvarlig for kvalitetssikring af de data, som indrapporteres af fiskerne i deres logbøger og landingstal i havne. Dette kvalitetsikres til dels ved, at Fiskerikontrollen fører fysisk kontrol til havs, i havne, og landing, og under transport af fisk og hos opkøbere af fisk.	Kvalitetssikring af data fra projektet er endnu ikke afklaret, men Fiskeristyrelsen vil have ansvaret for, at data gennemgår en fornøden kvalitetssikring.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	DTU Aqua deltager i internationale arbejdsgrupper omkring kvalitetssikring og ensretning af de standard moniteringstogter som der gennemføres. Det er altid personale fra DTU Aqua der deltager på togterne og kvalitetssikre data. Alt data indsamlet på togterne bliver indtastet og gemt i DTU Aquas databaser.	Data quality control systems of relevant data sources.	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	ICES WGBFAS	Quality control incorporated to national monitoring	Quality control - https://stat.luke.fi/en/commercial-marine-fishery	Duomenų kokybė užtikrinama atliekant pirminę duomenų kokybės apžiūrą, braižomi ilgio, svorio, amžiaus priklausomybių grafikai, vertinama, ar mėginio ir submėginio duomenys sutampa. Ekspertai dalyvauja darbo grupėse WGBIFS, WGBFAS ir RCG (Regional Coordination Group).	QA: Common HELCOM quality assurance programme: still missing. Analysis of information in the relevant ICES working groups (WGBFAS, WGIAB) and within the Advisory Committee (ACOM). Once in a 3-4 years in-depth stock assessment meetings (benchmark assessment) in which the data and valuation methods used in the calculations are examined in depth. QC: Analysis of information in the relevant ICES working groups (WGBFAS, WGBIFS) and within the Advisory Committee (ACOM).	QA: Common HELCOM quality assurance programme: still missing. Analysis of information in the relevant ICES working groups (WGBFAS, WGIAB) and within the Advisory Committee (ACOM). Once in a 3-4 years in-depth stock assessment meetings (benchmark assessment) in which the data and valuation methods used in the calculations are examined in depth. QC: Analysis of information in the relevant ICES working groups (WGBFAS, WGBIFS) and within the Advisory Committee (ACOM).	QA: Common HELCOM quality assurance programme: still missing. Analysis of information in the relevant ICES working groups (WGBFAS, WGIAB) and within the Advisory Committee (ACOM). Once in a 3-4 years in-depth stock assessment meetings (benchmark assessment) in which the data and valuation methods used in the calculations are examined in depth. QC: Analysis of information in the relevant ICES working groups (WGBFAS, WGBIFS) and within the Advisory Committee (ACOM).	Screening programme ICES DATRAS centre	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.	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.	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	Monitoring programmes are reviewed within ICES groups (trawl surveys) and/or through evaluations by the European Commission's Scientific, Technical and Economic Committee for Fisheries (STECF). Data is registered in the national database FISKDATA2 according to the updated manual. The quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers). Data from trawl surveys are delivered to ICES database DATRAS. Before data is accepted into DATRAS, delivered data undergoes quality review. Quality assurance of age reading and determination of sexual maturity of fish takes place through annual calibrations.	ICES data center data type guidelines and reference images are used for quality assurance. Linns CCC is used as quality control of data to check that the counting is consistent between stations.
Data management	The Federal Government/LÃ¤nder Working Group on the North Sea and the Baltic Sea (BLANO) is currently developing a national data management plan to support, in particular, the reporting and implementation of the MSFD. It takes into account existing target systems, such as the submission of data to ICES (for OSPAR and HELCOM), other EU directives and the provision of services to INSPIRE. To this end, various data management tools, such as a National Marine Catalogue (NMDK) or the coordination of data retention of geospatial, meta and time series data, are foreseen. The data are provided on a decentralised basis or centrally by the Marine Environment Database (MUDAB) by the various federal structures in the coastal LÃ¤nder, federal and research institutions. However, individual data sets are not yet freely available.	Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten sind auf dem Server des Thünen Instituts gespeichert.	Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die erhobenen Daten sind sowohl auf dem Server des Thünen Instituts für Ostseefischerei als auch auf dem ICES Server gespeichert. Die Daten können direkt auf der ICES Internetseite heruntergeladen werden.	Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten sind sowohl auf dem Server des Thünen Instituts für Ostseefischerei als auch beim ICES gespeichert.	Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten sind sowohl auf dem Server des Thünen Institits für Ostseefischerei als auch beim ICES gespeichert.	Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten sind auf dem Server des Thünen Institits für Ostseefischerei gespeichert.	Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten sind auf dem Server des Thünen Institits für Ostseefischerei gespeichert.	Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten liegen im Landesamt für Landwirtschaft, Lebensmittelsicherheit und Fischerei M-V intern vor und können auf Nachfrage angefordert werden.													The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	National databases and submissions to ICES DATRAS and ICES Acoustic trawl surveys database.	National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist	Duomenys kaupiami Klaipėdos universiteto Jūrų tyrimų institute http://apc.ku.lt/en/. Duomenys iš BITS reisų teikiami į ICES DATRAS, iš akustikos reisų – į ICES Acoustic trawl surveys duomenų bazę, versliniai duomenys eina į ICES InterCatch ir RDB duomenų bazes	Data holder is Institute of Food Safety, Animal Health and Environment BIOR and ICES. Results of biological analysis of samples collected in ports and from fishermen are entered in the relevant databases (Regional DataBase FishFrame, InterCatch). Data collected in international trawling surveys are stored in ICES international database DATRAS. QA/QC on data Data are available in ICES/Regional DataBase (RDB) DATRAS/BASS_DB, BIAS_DB/ INTERCATCH/BIOR. Common HELCOM database is under development.	Data holder is Institute of Food Safety, Animal Health and Environment BIOR and ICES. Results of biological analysis of samples collected in ports and from fishermen are entered in the relevant databases (Regional DataBase FishFrame, InterCatch). Data collected in international trawling surveys are stored in ICES international database DATRAS. QA/QC on data Data are available in ICES/Regional DataBase (RDB) DATRAS/BASS_DB, BIAS_DB/ INTERCATCH/BIOR Common HELCOM database is under development.	Data holder is Institute of Food Safety, Animal Health and Environment BIOR and ICES. Results of biological analysis of samples collected in ports and from fishermen are entered in the relevant databases (Regional DataBase FishFrame, InterCatch). Data collected in international trawling surveys are stored in ICES international database DATRAS. QA/QC on data Data are available in ICES/Regional DataBase (RDB) DATRAS/BASS_DB, BIAS_DB/ INTERCATCH/BIOR Common HELCOM database is under development.			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.	The raw data collected is stored in SLU Aqua's databases KUL (nets and vendace) and Fiskdata2 (coastal trawling in the North Sea). Data is updated annually and aggregated data is made available upon request to datavard-fisk@slu.se. Common international data is stored at ICES.		Raw data is stored at SLU Aqua. This data is updated annually and aggregated data is made available upon request. Common international data is stored at ICES
Data access	https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/48,https://www.thuenen.de/de/of/	https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/48,https://www.thuenen.de/de/of/	https://datras.ices.dk/Data_products/Download/Download_Data_public.aspx,https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/48,https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/8	https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/48,https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/8,https://www.thuenen.de/de/of/	https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/48,https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/8,https://www.thuenen.de/de/of/	https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/48,https://www.thuenen.de/de/of/	https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/48,https://www.thuenen.de/de/of/	https://mhb.meeresschutz.info/de/kennblaetter/neue-kennblaetter/details/pid/8	http://ices.dk/data/data-portals/Pages/DATRAS.aspx	http://ices.dk/data/data-portals/Pages/DATRAS.aspx	http://ices.dk/data/data-portals/Pages/DATRAS.aspx	http://ices.dk/data/data-portals/Pages/DATRAS.aspx	https://www.aqua.dtu.dk/	https://fiskeristyrelsen.dk/	https://fiskeristyrelsen.dk/	http://ices.dk/data/data-portals/Pages/acoustic.aspx	http://ices.dk/data/data-portals/Pages/acoustic.aspx	https://www.aqua.dtu.dk/	https://www.aqua.dtu.dk/	http://ices.dk/data/data-portals/Pages/acoustic.aspx	http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	http://ices.dk/data/dataset-collections/Pages/Fish-trawl-survey.aspx,https://www.ices.dk/data/dataset-collections/Pages/HELCOM.aspx	http://www.ely-keskus.fi/web/ely/saalisseuranta,https://stat.luke.fi/en/uusi-etusivu,https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06%20Kala%20ja%20riista__02%20Rakenne%20ja%20tuotanto__02%20Kaupallinen%20kalastus%20merella/?tablelist=true&rxid=0266bbbe-b8bd-4491-bcf6-90622cf7ca35	http://www.ices.dk/data/dataset-collections/Pages/Fish-catch-and-stock-assessment.aspx	https://www.ices.dk/data/data-portals/pages/DATRAS.aspx	https://www.ices.dk/data/data-portals/pages/DATRAS.aspx	https://www.ices.dk/data/data-portals/pages/DATRAS.aspx	http://ekoinfonet.gios.gov.pl/Ichtiofauna/faces/Logowanie?_adf.ctrl-state=2dlbblto5_3,https://www.ices.dk/data/data-portals/Pages/DATRAS.aspx	https://www.havochvatten.se/marin-miljoovervakning-bifangst-data	https://www.havochvatten.se/marin-miljoovervakning-kontroll-fiskeriverksamhet-data	https://www.slu.se/institutioner/akvatiska-resurser/databaser/kul/	https://www.havochvatten.se/marin-miljoovervakning-fritidsfiske-data	https://www.havochvatten.se/marin-miljoovervakning-migrerande-lax-data	https://www.havochvatten.se/marin-miljoovervakning-kustfisk-data	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon-data	https://www.havochvatten.se/marin-miljoovervakning-djur-havsbotten-data
Related indicator/name		Cod (Gadus morhua) in Subdivisions 22-24, western Baltic stock (western Baltic Sea)					Cod (Gadus morhua) in Subarea 4 and Divisions 7.d and 20 (North Sea, eastern English Channel, Skagerrak) Cod (Gadus morhua) in Subdivisions 22-24, western Baltic stock (western Baltic Sea)		Vurderingen af fiskeriet af kommercielle fisk Vurderingsark vedr. D4C2	Vurderingen af fiskeriet af kommercielle fisk Vurderingsark vedr. D4C2	Vurderingen af fiskeriet af kommercielle fisk Vurderingsark vedr. D4C2	Vurderingen af fiskeriet af kommercielle fisk Vurderingsark vedr. D4C2	Trends in bycatch of non-commercially exploited fish	Vurderingen af fiskeriet af kommercielle fisk Trends in bycatch of non-commercially exploited fish Vurderingsark vedr. D4C2		Vurderingen af fiskeriet af kommercielle fisk Vurderingsark vedr. D4C2	Vurderingen af fiskeriet af kommercielle fisk Vurderingsark vedr. D4C2	Vurderingen af fiskeriet af kommercielle fisk Vurderingsark vedr. D4C2	Vurderingen af fiskeriet af kommercielle fisk Vurderingsark vedr. D4C2			95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	Fishing mortality (F) of Baltic sprat (Sprattus sprattus balticus) Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32) Spawning stock biomass (SSB) of Baltic sprat (Sprattus sprattus balticus) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32)	Abundance of Sea Trout Spawners and Parr Eastern cod stock and fishing mortality Herring stock and fishing mortality in Central Baltic Herring stock and fishing mortality in Gulf of Bothnia Sprat stock and fishing mortality Abundance of Salmon spawners and smolt Number of drowned mammals and waterbirds in fishing gear Catch of Perch and Pike-Perch Whitefish size distribution Selective fishing intensity on sea trouts	Abundance of Key Coastal Fish Species Abundance of Sea Trout Spawners and Parr Abundance of coastal fish key functional groups Abundance of Salmon spawners and smolt Number of drowned mammals and waterbirds in fishing gear Catch of Perch and Pike-Perch	5 cm) 95-asis žuvų ilgio pasiskirstymo procentilis remiantis mokslinių tyrimų laivų įrašais: brėtlingis (Sprattus sprattus) 95-asis žuvų ilgio pasiskirstymo procentilis remiantis mokslinių tyrimų laivų įrašais: menkė (Gadus morhua) 95-asis žuvų ilgio pasiskirstymo procentilis remiantis mokslinių tyrimų laivų įrašais: plekšnė (Platichthys flesus) 95-asis žuvų ilgio pasiskirstymo procentilis remiantis mokslinių tyrimų laivų įrašais: strimelė (Clupea harengus) Didesnių už vidutinę pirmos lytinės brandos normą žuvų proporcija: brėtlingis (Sprattus sprattus) (>12 cm) Didesnių už vidutinę pirmos lytinės brandos normą žuvų proporcija: menkė (Gadus morhua) (>35 cm) Didesnių už vidutinę pirmos lytinės brandos normą žuvų proporcija: plekšnė (Platichthys flesus) (>21,5 cm) Didesnių už vidutinę pirmos lytinės brandos normą žuvų proporcija: strimelė (Clupea harengus) (>16 cm) Mirtingumo dėl žvejybos koeficientas: brėtlingiui (Sprattus sprattus) Mirtingumo dėl žvejybos koeficientas: menkei (Gadus morhua) Mirtingumo dėl žvejybos koeficientas: strimelei (Clupea harengus) Neršiančių išteklių biomasė: brėtlingiui (Sprattus sprattus) Neršiančių išteklių biomasė: menkei (Gadus morhua) Neršiančių išteklių biomasė: strimelei (Clupea harengus)	Fishing mortality AGE-D F FishCommercial MOR SIZE-D	Spawning stock biomass AGE-D BIOM FishCommercial SIZE-D	AGE-D BIOM FishCommercial SIZE-D	ICES stock assessment ICES stock assessment ICES stock assessment ICES stock assessment ICES stock assessment	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-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		1.2F Förekomst av nyckelart av fisk i kustvatten – abborre och skrubbskädda/ 1.2F Abundance of key fish species in coastal waters - perch and flounder 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 4.2A Abundans av viktiga funktionella grupper av fisk i kustvatten - rovfisk och karpfisk/ 4.2A Abundance of important functional fish groups in coastal waters C.4.2 Storleksstruktur hos nyckelart i kustvatten - torsk/ C.4.2 Size structure in key fish species in coastal waters – cod C.4.3 Storleksstruktur hos nyckelart av fisk i kustvatten – abborre / C.4.3 Size structure in key fish species in coastal waters - perch 1.2G Förekomst av nyckelart av fisk i kustvatten – abundans av stor torsk/ 1.2G Abundance of key fish species in coastal waters - large cod 1.3C Andel stor bottenlevande fisk i fjord- och skärgårdsområden/ 1.3C Proportion of large demersal fish (LFI) in fjord and archipelago areas ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter	1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 1.2H Lekbiomassa (SSB) för pelagiska och demersala fiskarter/ 1.2H Spawning stock biomass (SSB) for pelagic and demersal fish species 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations 3.2A Lekbiomassa (SSB) för alla kommersiellt nyttjade populationer/ 3.2A Spawning stock biomass (SSB) for all commercially exploited populations ANSSE-3.1A_Fiskerid�dlighet ANSSE-C.3.2_Lekbiomassa_kom_best�nd ANSSE-C.3.3_H�llbart_nyttjande_arter ANSSE-C.4.1_Storleksstruktur_fisk_utsj� BALSE-3.1A_Fiskerid�dlighet BALSE-C.3.2_Lekbiomassa_kom_best�nd BALSE-C.3.3_H�llbart_nyttjande_arter BALSE-C.4.1_Storleksstruktur_fisk_utsj�
Contact	Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de	Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de	Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de	Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de	Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de	Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de	Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de	Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de	DTU Aqua aqua@aqua.dtu.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua aqua@aqua.dtu.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua https://www.aqua.dtu.dk/ Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua https://www.aqua.dtu.dk/ Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua aqua@aqua.dtu.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk	Fiskeristyrelsen mail@fiskeristyrelsen.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua aqua@aqua.dtu.dk Fiskeristyrelsen mail@fiskeristyrelsen.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua aqua@aqua.dtu.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua aqua@aqua.dtu.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua aqua@aqua.dtu.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua aqua@aqua.dtu.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk	DTU Aqua aqua@aqua.dtu.dk Miljøstyrelsen masjo@mst.dk kregn@mst.dk		Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.				Institute of Food Safety, Animal Health and Environment BIOR:	Institute of Food Safety, Animal Health and Environment BIOR:	Institute of Food Safety, Animal Health and Environment BIOR:		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	\|\| MP_86 \|\| --# Krumme U, Gröhsler T (2013) Analysis of the questionaires concerning the issue of species misreporting in the mixed pelagic fisheries in the Baltic Sea (sprat-herring mix). In: Report of the Benchmark Workshop on Baltic Multispecies Assessments (WKBALT): 4-8 February 2013. Copenhagen: ICES, pp 266-276 Krumme U, Gröhsler T (2013) Sprat (BS)/Central Baltic Herring (CBH): Analysis of the questionnaires concerning the issue of species misreportning in the mixed pelagic fisheries in the Baltic Sea (sprat-herring mix). In: Report of the Benchmark Workshop on Baltic Multispecies Assessments (WKBALT): 4-8 February 2013. Copenhagen: ICES, pp 266-276 # #--	\|\| MP_137 \|\| --# Hyder K, Weltersbach MS, Armstrong M, Strehlow HV, et al (2018) Recreational sea fishing in Europe in a global context : participation rates, fishing effort, expenditure, and implications for monitoring and assessment. Fish Fisheries 19(2):225-243, DOI:10.1111/faf.12251 Radford Z, Hyder K, Zarauz L, Mugerza E, Ferter K, Prellezo R, Strehlow HV, Townhill B, Lewin W-C, Weltersbach MS (2018) The impact of marine recreational fishing on key fish stocks in European waters. PLoS One 13(9):e0201666, DOI:10.1371/journal.pone.0201666 Strehlow HV (2017) Die Sache mit dem Angelhaken .... Meer Küste(6):21 Strehlow HV, Weltersbach MS (2017) Jobmotor Meeresangeln - Zwei aktuelle Studien belegen: Meeresangeln ist ein bedeutender Wirtschaftsfaktor in Europa [online]. Fischerei Fischmarkt MV(4):38-40 # #--	\|\| MP_77 \|\| --# Die Daten wurden bereits für mehrere Publikationen genutzt. Das "Manual for the Baltic International Trawl Surveys (BITS)" kann auf der Internetseite des ICES heruntergeladen werden. # https://www.ices.dk/marine-data/data-portals/Pages/DATRAS-Docs.aspx #--	\|\| MP_79 \|\| --# Schaber M, Gröhsler T (2019) Survey report for FRV SOLEA / German Acoustic Autumn Survey (GERAS): 01 - 19 October 2018. ICES Sci Rep 1(11):190-224 # http://www.ices.dk/community/groups/Pages/WGBIFS.aspx #--	\|\| MP_82 \|\| --# http://www.ices.dk/community/groups/Pages/WGIPS.aspx #--	\|\| MP_83 \|\| --# #--	\|\| MP_85 \|\| --# Stroganov AN, Bleil M, Oeberst R, Semenova AV, Winkler H (2018) First evidence of spawning of eastern Baltic cod (Gadus morhua callarias) in the Belt Sea, the main spawning area of western Baltic cod (Gadus morhua L.). J Appl Ichthyol 34(3):527-534, DOI:10.1111/jai.13550 Velasco A, Bleil M (2016) Bericht über die 716.+ 717. Reise des FFS "Solea" vom 18.2. bis 10.3.2016 : Baltic International Trawl Spring Survey (BITS) in der Arkonasee, Mecklenburger- und Kieler Bucht (ICES SD FFS24+22). Rostock: Thünen-Institut für Ostseefischerei, 10 p Bleil M, Velasco A (2016) Bericht über die 721. Reise des FFS Selea vom 13.06. bis 20.06.2016 : Untersuchungen zur Laicherbestandsstruktur, zum Anteil aktiver Laicher. zu Kondition und Laichaktivitäten und zur Reifeentwicklung von Dorschen in Beziehung zur hydrographischen Situation in der zentralen Ostsee (COBALT). Rostock: Thünen-Institut für Ostseefischerei, 6 p # #--	\|\| MP_89 \|\| --# https://www.lallf.de/fischerei/fischereischutz/besatzmassnahmen/ #--	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).				Latvian National Fisheries and Aquaculture Data Collection Work Plan: https://datacollection.jrc.ec.europa.eu/wp/2020) Manual for the Baltic International Trawl Surveys (BITS). Version 2.0 (WGBIFS, 2017), http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP7%20BITS%202017.pdf Manual for the International Baltic Acoustic Surveys (IBAS) Version 2.0 (WGBIFS, 2017), http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP%208%20IBAS%202017.pdf BIOR guidelines/methods: - Methods of collecting biological samples from fishing vessels by random choice: https://www.bior.lv/sites/default/files/inline-files/Random_sampling.pdf - Manual for observers on the Baltic Sea on Latvian fishing vessels https://www.bior.lv/sites/default/files/inline-files/Guidelines_observer_Baltic.pdf - Sampling biological cod during industrial: https://www.bior.lv/sites/default/files/inline-files/Latvia_cod_sampling.pdf - Sampling of flounder biological material during industrial surveys: https://www.bior.lv/sites/default/files/inline-files/Latvia_flounder_sampling.pdf - Method for data collection during the recreational fishing in the sea: https://www.bior.lv/sites/default/files/inline-files/Atputas_zvejas_uzskaite_jura.pdf	Latvian National Fisheries and Aquaculture Data Collection Work Plan: https://datacollection.jrc.ec.europa.eu/wp/2020) Manual for the Baltic International Trawl Surveys (BITS). Version 2.0 (WGBIFS, 2017), http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP7%20BITS%202017.pdf Manual for the International Baltic Acoustic Surveys (IBAS) Version 2.0 (WGBIFS, 2017), http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP%208%20IBAS%202017.pdf. BIOR guidelines/methods: - Methods of collecting biological samples from fishing vessels by random choice: https://www.bior.lv/sites/default/files/inline-files/Random_sampling.pdf. - Manual for observers on the Baltic Sea on Latvian fishing vessels: https://www.bior.lv/sites/default/files/inline-files/Guidelines_observer_Baltic.pdf - Sampling biological cod during industrial: https://www.bior.lv/sites/default/files/inline-files/Latvia_cod_sampling.pdf - Sampling of flounder biological material during industrial surveys: https://www.bior.lv/sites/default/files/inline-files/Latvia_flounder_sampling.pdf.	Latvian National Fisheries and Aquaculture Data Collection Work Plan: https://datacollection.jrc.ec.europa.eu/wp/2020) Manual for the Baltic International Trawl Surveys (BITS). Version 2.0 (WGBIFS, 2017), http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP7%20BITS%202017.pdf Manual for the International Baltic Acoustic Surveys (IBAS) Version 2.0 (WGBIFS, 2017), http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP%208%20IBAS%202017.pdf BIOR guidelines/methods: - Methods of collecting biological samples from fishing vessels by random choice: https://www.bior.lv/sites/default/files/inline-files/Random_sampling.pdf - Manual for observers on the Baltic Sea on Latvian fishing vessels https://www.bior.lv/sites/default/files/inline-files/Guidelines_observer_Baltic.pdf - Sampling biological cod during industrial: https://www.bior.lv/sites/default/files/inline-files/Latvia_cod_sampling.pdf - Sampling of flounder biological material during industrial surveys: https://www.bior.lv/sites/default/files/inline-files/Latvia_flounder_sampling.pdf - Method for data collection during the recreational fishing in the sea: https://www.bior.lv/sites/default/files/inline-files/Atputas_zvejas_uzskaite_jura.pdf		https://www.havochvatten.se/marin-miljoovervakning-bifangst	https://www.havochvatten.se/marin-miljoovervakning-kontroll-fiskeriverksamhet	https://www.havochvatten.se/marin-miljoovervakning-migrerande-al	https://www.havochvatten.se/marin-miljoovervakning-fritidsfiske	https://www.havochvatten.se/marin-miljoovervakning-migrerande-lax	https://www.havochvatten.se/marin-miljoovervakning-kustfisk	https://www.havochvatten.se/marin-miljoovervakning-fisk-utsjon	https://www.havochvatten.se/marin-miljoovervakning-djur-havsbotten