MS/Art8/2018/D1-R/Spain/NE Atlantic: Bay of Biscay & Iberian Coast

Member State report / Art8 / 2018 / D1-R / Spain / NE Atlantic: Bay of Biscay & Iberian Coast

Report type	Member State report to Commission
MSFD Article	Art. 8 Initial assessment (and Art. 17 updates)
Report due	2018-10-15
GES Descriptor	D1 Reptiles
Member State	Spain
Region/subregion	NE Atlantic: Bay of Biscay & Iberian Coast
Reported by	Subdirección General para la protección del mar. D.G. Sostenibilidad de la Costa y del Mar. Minister
Report date	2020-02-03
Report access	msfd2018-ART8GES_MOD2020.xml

Demarcación marina noratlántica (ABI-ES-SD-NOR)

Simplified table

GES component	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R
Feature	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles
Element	Caretta caretta	Caretta caretta	Caretta caretta	Caretta caretta	Caretta caretta	Caretta caretta	Dermochelys coriacea	Dermochelys coriacea	Dermochelys coriacea	Dermochelys coriacea	Dermochelys coriacea	Dermochelys coriacea
Element code	137205	137205	137205	137205	137205	137205	137209	137209	137209	137209	137209	137209
Element code source	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D1C1	D1C2	D1C3	D1C4	D1C5	D1C5	D1C1	D1C2	D1C3	D1C4	D1C5	D1C5
Parameter	Mortality rate / Mortality rate from fishing (F)	Abundance		Distribution (range)	Extent	Habitat condition	Mortality rate / Mortality rate from fishing (F)	Abundance		Distribution (range)	Extent	Habitat condition
Parameter other
Threshold value upper	0.2			100.0	100.0	100.0				100.0	100.0	100.0
Threshold value lower
Threshold qualitative
Threshold value source	Other (specify)			Other (specify)		Other (specify)				Other (specify)	Other (specify)	Other (specify)
Threshold value source other	Heppill et al. (2002 and 2003			Mansfield et al. (2014)		Mansfield et al. (2014)				Eckert (2006)	Eckert (2006)	Eckert (2006)
Value achieved upper					100.0	100.0
Value achieved lower
Value unit	Other	Other		percentage	Other		Other	Other		percentage	Other	Other
Value unit other	Annualised mortality rate	TURTELS/KM2			PERCENTAGE		Annualised mortality rate	TURTELS/KM2			PERCENTAGE	PERCENTAGE
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown		Unknown	Stable	Stable	Unknown	Unknown		Unknown	Stable	Stable
Parameter achieved	Not assessed	Not assessed		Not assessed	Yes	Yes	Not assessed	Not assessed		Not assessed	Yes	Yes
Description parameter
Related indicator
Criteria status	Not assessed	Unknown	Not assessed	Not assessed	Good	Good	Not assessed	Not assessed	Not assessed	Not assessed	Good	Good
Description criteria		Density will be assessed when the final results of the 2018 ACCOBAMS surevy wil be published			Proportion of oceanographic buoys where the surface temperature of seawater exceeds 20ºC in the months of July, August or September.	Proportion of oceanographic buoys where the surface temperature of seawater exceeds 20ºC in the months of July, August or September.		No leadtherback turtles was observed during the 2018 ACCOBAMS surevy			Upwelelling index as resting by IEO, >Â 300 m3s-1Â km-1	Upwelelling index as resting by IEO, >Â 300 m3s-1Â km-1
Element status	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Description element
Integration rule type parameter	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description parameter
Integration rule type criteria	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI
Integration rule description criteria	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Description overall status	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.
Assessments period	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018
Related pressures	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Related targets	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8	A.N.1 A.N.10 A.N.11 A.N.2 A.N.3 A.N.5 A.N.6 A.N.7 A.N.8 A.N.9 B.N.14 B.N.15 C.N.15 C.N.16 C.N.17 C.N.18 C.N.3 C.N.4 C.N.6 C.N.7 C.N.8

Demarcación marina sudatlántica (ABI-ES-SD-SUD)

Simplified table

GES component	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R	D1-R
Feature	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles	Turtles
Element	Caretta caretta	Caretta caretta	Caretta caretta	Caretta caretta	Caretta caretta	Caretta caretta	Dermochelys coriacea	Dermochelys coriacea	Dermochelys coriacea	Dermochelys coriacea	Dermochelys coriacea	Dermochelys coriacea
Element code	137205	137205	137205	137205	137205	137205	137209	137209	137209	137209	137209	137209
Element code source	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D1C1	D1C2	D1C3	D1C4	D1C5	D1C5	D1C1	D1C2	D1C3	D1C4	D1C5	D1C5
Parameter	Mortality rate / Mortality rate from fishing (F)	Abundance		Distribution (range)	Extent	Habitat condition	Mortality rate / Mortality rate from fishing (F)	Abundance		Distribution (range)	Extent	Habitat condition
Parameter other
Threshold value upper	0.2			100.0						100.0
Threshold value lower
Threshold qualitative
Threshold value source	Other (specify)			Other (specify)						Other (specify)
Threshold value source other	Heppill et al. (2002 and 2003			Cejudo et al. (2006); Eckert (2008)						Eckert (2006)
Value achieved upper				100.0
Value achieved lower
Value unit	Other	Other		percentage			Other	Other		percentage
Value unit other	Annualised mortality rate	TURTELS/KM2					MR DEEDS	TURTELS/KM2
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown		Unknown	Unknown	Unknown	Unknown	Unknown		Unknown	Unknown	Unknown
Parameter achieved	Not assessed	Not assessed		Yes	Not assessed	Not assessed	Not assessed	No		No	Not assessed	Not assessed
Description parameter
Related indicator
Criteria status	Not assessed	Unknown	Not assessed	Good	Not assessed	Not assessed	Not assessed	Not good	Not assessed	Not good	Not assessed	Not assessed
Description criteria		Density will be assessed when the final results of the 2018 ACCOBAMS surevy wil be published		Hard-shelled turtles observed through the area during the 2018 ACCOBAMS survey				No leadtherback turtles was observed during the 2018 ACCOBAMS surevy		No leadtherback turtles was observed during the 2018 ACCOBAMS surevy
Element status	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Description element
Integration rule type parameter	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description parameter
Integration rule type criteria	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI	HIE_NWEI
Integration rule description criteria	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.	HIE_NWEi: If a primary criterion cannot be assessed for a species due to a lack of data then the resultant assessment of that criterion for the species cannot be assigned a status (i.e. it is ‘not assessed’). Where the species is only assessed with the primary abundance criterion, if data are missing for this criterion, the species cannot be assigned a status. It also means that the Member State should take action on monitoring and assessment tools to ensure that at the next update under Article 8 MSFD an assessment can be undertaken. At least D1C1 and D1C4 (50%) have to be fulfilled for both species to achieve GES. If one species is missing in the area (D1C4), GES cannot be Good. GES cannot be assessed only on the basis of D1C5.
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Description overall status	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.	No conclusion on the overall status can be achieved in the absence of data about the mortality rate.
Assessments period	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018	2012-2018
Related pressures	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Related targets	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8	A.S.1 A.S.10 A.S.12 A.S.2 A.S.3 A.S.4 A.S.5 A.S.6 A.S.7 A.S.8 B.S.14 B.S.15 C.S.10 C.S.11 C.S.15 C.S.16 C.S.17 C.S.18 C.S.3 C.S.4 C.S.6 C.S.7 C.S.8