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

Member State report / Art8 / 2018 / D1-M / 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 Mammals
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-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M
Feature	Baleen whales	Baleen whales	Baleen whales	Baleen whales	Baleen whales	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Deep-diving toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans
Element	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Globicephala melas	Globicephala melas	Globicephala melas	Globicephala melas	Globicephala melas	Globicephala melas	Globicephala melas	Ziphius cavirostris	Ziphius cavirostris	Ziphius cavirostris	Ziphius cavirostris	Ziphius cavirostris	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Phocoena phocoena (Linnaeus 1758) [Harbour porpoise]	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus
Element code	137091	137091	137091	137091	137091	137097	137097	137097	137097	137097	137097	137097	137127	137127	137127	137127	137127	137094	137094	137094	137094	137094	137094	137094	137094	137094	137094	137094	137117	137117	137117	137117	137117	137117	137117	137117	137117	137117	137117	137111	137111	137111	137111	137111	137111	137111	137111	137111	137111	137111	137111	137111	137111	137111	137111
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/	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/	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/	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/	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	UG21-BP Atlanac population	UG21-BP Atlanac population	UG21-BP Atlanac population	UG21-BP Atlanac population	UG21-BP Atlanac population	UG13-GM Atlantic population	UG13-GM Atlantic population	UG13-GM Atlantic population	UG13-GM Atlantic population	UG13-GM Atlantic population	UG13-GM Atlantic population	UG13-GM Atlantic population	Agricultural population	Agricultural population	Agricultural population	Agricultural population	Agricultural population												G1: The Iberian population	G1: The Iberian population	G1: The Iberian population	G1: The Iberian population	G1: The Iberian population	G1: The Iberian population	G1: The Iberian population	G1: The Iberian population	G1: The Iberian population	G1: The Iberian population	G1: The Iberian population									UG2-TT coal waters south Galicia	UG2-TT coal waters south Galicia	UG2-TT coal waters south Galicia	UG2-TT coal waters south Galicia	UG2-TT coal waters south Galicia	UG2-TT coal waters south Galicia	UG2-TT coal waters south Galicia	UG2-TT coal waters south Galicia
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D1C1	D1C2	D1C3	D1C4	D1C5	D1C1	D1C2	D1C3	D1C4	D1C5	D1C5	D1C5	D1C1	D1C2	D1C3	D1C4	D1C5	D1C1	D1C1	D1C2	D1C3	D1C3	D1C3	D1C3	D1C3	D1C3	D1C4	D1C5	D1C1	D1C1	D1C2	D1C3	D1C3	D1C3	D1C3	D1C3	D1C4	D1C5	D1C5	D1C1	D1C1	D1C2	D1C3	D1C3	D1C4	D1C5	D1C5	D1C1	D1C1	D1C2	D1C3	D1C3	D1C4	D1C5	D1C5
Parameter	Mortality rate / Mortality rate from fishing (F)	Abundance	Age distribution	Distribution (pattern)	Habitat condition	Other	Abundance	Age distribution	Distribution (spatial)	Other	Other	Other	Mortality rate / Mortality rate from fishing (F)	Abundance	Age distribution	Distribution (pattern)	Habitat condition	Mortality rate / Mortality rate from fishing (F)	Other	Abundance	Age distribution	Other	Other	Other	Other	Sex distribution	Distribution (spatial)	Other	Mortality rate / Mortality rate from fishing (F)	Other	Abundance	Age distribution	Other	Other	Other	Sex distribution	Distribution (spatial)	Extent	Habitat condition	Mortality rate / Mortality rate from fishing (F)	Other	Abundance	Other	Survival rate	Distribution (spatial)	Other	Other	Mortality rate / Mortality rate from fishing (F)	Other	Abundance	Other	Survival rate	Distribution (pattern)	Other	Other
Parameter other						Percentage of stranded pilot whales with signals compatible with bycatch.				CON-B-Li	CONC-B-FA	CONC-B-OT							Percentage of stranded common dolphins with signals compatible with bycatch			AGR- Annual Management Rate	Life ExPecancy	NMR- Natural Mortality Rate	Ise- length			Indirect values of contanmats available		Percentage of stranded porpoises with signals compatible with bycatch			annual measurement AGR	Breeding interval BI	size-length						Percentage of stranded boltenose dolphins with signals compatible with bycatch		temporal emigration probability (TEP) estimated for the Ria de Arousa area			CONC-B-LI	CONC-B-OT		Percentage of stranded boltenose dolphins with signals compatible with bycatch		temporal emigration probability (TEP) estimated for the Ria de Arousa area			CONC-B-LI	CONC-B-OT
Threshold value upper																												17.0
Threshold value lower
Threshold qualitative																		Number of individuals dead due to bycatch never exceed 0.7% of the best abundance estimate available.											Number of individuals dead due to bycatch never exceed 1.7% of the best abundance estimate available.		not assessed	not assessed								Number of individuals dead due to bycatch never exceed 1.4% of the best abundance estimate available.								Number of individuals dead due to bycatch never exceed 1.4% of the best abundance estimate available.
Threshold value source																		OSPAR Convention	Other (specify)										Other (specify)	OSPAR Convention				National	National					OSPAR Convention	Other (specify)							OSPAR Convention	Other (specify)
Threshold value source other																			Annual mortality rate due to bycatch is reduced below 0.7% of the best population estimate										Annual mortality rate due to bycatch is reduced below 1.7% of the best population estimate												Annual mortality rate due to bycatch is reduced below 1.4% of the best population estimate								Annual mortality rate due to bycatch is reduced below 1.4% of the best population estimate
Value achieved upper						27.6				31.0	50.0	30.0						53.0	53.08		29.0	37.5	7.2	12.8	252.0	50.0			11.0	48.6			0.53	1.8		50.0				18.3	25.6	4118.0				19.1	5.7	18.3	25.6	144.0	0.68	1.0		19.1	5.7
Value achieved lower																						33.2							4.3													2471.0								56.0
Value unit		(number of) individuals				percentage				Other	percentage	Other		(number of) individuals				Other	percentage	(number of) individuals		percentage	Other	percentage	centimetre	Other	Other	Other	Other	percentage	(number of) individuals	Other	Other	Other	centimetre	Other	Other			Other	percentage	(number of) individuals			Other	Other	Other	Other	percentage	(number of) individuals			Other	Other	Other
Value unit other										MICROGREAME/GRAME		MICROGREAME/GRAME						%					years			% females/males	Seasonal fluctuations in abundance with minimun values in autum and maximun in winter/spring	gram/grame	%			years	Calves/year	years		% females/males	Increasing hardship from East to West			%					Seasonal fluctuations in abundance with minimun values in autum and maximun in winter/spring	gram/grame	gram/grame	%					Seasonal fluctuations in abundance with minimun values in autum and maximun in winter/spring	gram/grame	gram/grame
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown
Parameter achieved	Not assessed	Not assessed	Unknown	Not assessed	Unknown	Not assessed	Not assessed	Unknown	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Unknown	Not assessed	Unknown	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Unknown	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	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 parameter		The abundances estimates availables never are reffered completelly to the DMNOR area, and the analitical methods, the survey platforms and the time period are different. García-Barón et al. (2016), single platform ship in Bay of Biscay in september 2013-2015. Hammond et al. (2017), circle back aerial survey and double platform ship survey carried out in continental shelf of iberian peninsula and deep waters of Bay of Biscay waters in july 2016. García-Barón et al. (2016), year 2013, 1350 individuals (CV: 0.28 ), year 2014, 1290 individuals (CV: 0.26), and year 2015 , 1270 individuos (CV: 0.30). Hammond et al. (2017). Block 11, 2052 individuals (CV: 0.22, 95%IC: 1254-3358), block 12, 1025 individuals (CV: 0.21, 95%IC: 648-1620), bloque 12, 3645 individuals (CV: 0.20, 95%IC: 2374-5594).		"García-Barón et al. (2016). High variability in the area between years. Hammond et al. (2017). Homogenously distributed in the Bay of Biscay and Galicia Bank.			The survey platforms and the time period of the abundances estimates availables are different. Santos et al. (2009), double platform ship and aerial survey in DMNOR area in july 2005 and 2007. Hammond et al. (2017), circle back aerial survey and double platform ship survey carried out in continental shelf of iberian peninsula and deep waters of Bay of Biscay waters in july 2016. Hammond et al. (2017). Block AA, 76 (CV: 1.09, 95%IC: 11-517) individuals. Block AC, 1917 (CV: 1.24, 95%IC: 273-13442) individuals. Block 11, 173 (CV: 1.11 , 95%IC: 19-1599) individuals. Block 12, 320 (CV: 0.71, 95%IC: 77-1322) individuals. Block 13, 4377 (CV: 0.64, 95%IC: 1283-14938) individuos.		"Santos et al. (2009).Higher density areas in northern limit of the slope and Galician Bank in july. Rogan et al. (2017). Preference of areas deeper than 1000 m in july. "	(MÃ©ndez-Fernrandez et al., 2013b	MÃ©ndez-Fernandez et al., 2014). CONC-B-FA: Less than 50Â % of individuals with valuations over 17 Î¼g/g	MÃ©ndez-Fernandez et al., 2014). WITH REGARD TO THE FOLLOWING: CD 30.0 Â±Â 26.9 Î¼g/g		The abundances estimates availables never are reffered completelly to the DMNOR area, and the analitical methods, the survey platforms and the time period are different. Canadas et al. (2011), double platform ship and aerial survey in deepm waters of Bay of Biscay and Galician bank in july 2007. Macleod et al. (2011), single platform ship survey in Torrelavega and Cap Breton canyos during july 2006,2007 and 2008. Hammond et al. (2017), Hammond et al. (2017), circle back aerial survey and double platform ship survey carried out in continental shelf of iberian peninsula and deep waters of Bay of Biscay waters in july 2016. Hammond et al. (2017). Block AC, 518 individuals (CV: 0.53, 95%IC: 212-1593) , bloque 11, 484 individuals (CV: 0.85, 95%IC: 108-2171), bloque 12, 255 individuals (CV: 0.63, 95%IC: 78-834) , bloque 13, 4244 individuals (CV: 0.63, 95%IC: 1317-13683) .		High density areas in deep canyons of Bay of Biscay				The abundances estimates availables never are reffered completelly to the DMNOR area, and the analitical methods, the survey platforms and the time period are different. Hammond et al. (2017), circle back aerial survey and ship survey carried out in continental shelf of iberian peninsula waters in july 2016. Saavedra (2017), ship survey carried out in Bay of Biscay waters in march-april betwen 2007 and 2016. Hammond et al. (2017). Continental shelf: Block AA, 18458 individuals (CV: 0.64, 95%IC: 3297-51064) individuals; block AB, 63243 individuals (CV: 0.27, 95%IC: 34978-103337) individuals; block AC, 71082 individuals (CV: 0.31, 95%IC: 36898-124302) individuals. Deep wasters Bay of Biscay: 11, 12, y 13, block 11, 34570 individuals (CV: 63, 95%IC: 8154-146570) individuals, block 12, 643 individuals (CV: 0.54, 95%IC: 206-2007) individuals y block 13, 3110 individuals (CV: 0.65, 95%IC: 861-11236) individuals. Saavedra (2017). Northern and northwester continental shelf waters. Conventional Distance Sampling method 12831 individuals (CV: 0.18, 95%IC: 9025-18242) individuals. Corrected for responsive movent and percpetion bias, 4747 individuals (CV: 0.19, 95%IC: 3307-6816) individuals. Corrected for responsive movement, 22510 individuals (CV: 0.18, 95%IC: 15776-32120) individuals.	AGE-D: 24 years of the substance and 29 years.				252Â cm femal and 240Â cm ills		Hammond et al. (2017), relativelly higer number of sightings in Galicia in july 2017. García-Barón et al. (2018) homogeneous distribution alongside the atlantic iberian continental shelf in septembre. Gutiérrez et al. (2018), maximum values in the eastern part of the atlantic iberian continental shelf , and minimun density values in western part druing march-april.	(Méndez-Fernandez et al., 2013b; Méndez-Fernández et al., 2014). Half of the animals that were analyzed presented values over the limit of 17 μg/g , indicating potencial health problems .	Annual mortality rate. 4.3-11-1%.		Hammond et al. (2017). Block AC 183 individuals (CV: 1.00, 95%IC: 0-669). Block AB 2715 individuals (CV: 0.31, 95%IC: 1350-4737). Martínez-Cedeira et al. (2016). Ship survey 1185 individuals (CV: 0.43, 95%IC: 512-2730). Aerial survey 186 individuals (95%IC: 40-854).	AGE-D: 18 years of the substance and 19 years			185Â cm femal and 162Â cm ills							The abundances estimates availables never are reffered completelly to the DMNOR area, and the analitical methods, the survey platforms and the time period are different. Hammond et al. (2017), circle back aerial survey carried out in continental shelf of iberian peninsula waters in july 2016. García-Barón et al. (2018), ship survey carried out in Bay of Biscay waters in september betwen 2009 and 2016. VALUE ACHIEVED UPPER: Hammond et al. (2017). Blocks AB (CV: 0.028, 95%IC: 0-1932) individuals; AC (CV: 0.12, 95%IC: 997-8529) individuals. García-Barón et al. (2018). Maximum values in 2009 (4472 individuals, CV: 0.86), 2013 (4118 individuals, CV: 0.79). VALUE ACHIEVED LOWER: Hammond et al. (2017). Blocks AB (CV: 0.028, 95%IC: 0-1932) individuals; AC (CV: 0.12, 95%IC: 997-8529) individuals. García-Barón et al. (2018). Minimum values in 2011 (2510 individuals, CV: 1.0) y 2014 (2471 individuals, CV: 0.97)			Hammond et al. (2017), relativelly higer number of sightings in Galicia in july 2017. García-Barón et al. (2018) homogeneous distribution alongside the atlantic iberian continental shelf in septembre. Gutiérrez et al. (2018), maximum values in the eastern part of the atlantic iberian continental shelf , and minimun density values in western part druing march-april.	(MÃ©ndez-Fernrandez et al., 2013b	(Méndez-Fernandez et al., 2013b; Méndez-Fernández et al., 2014). CONC-B-OT: Cd 5.7±13.8 μg/g			There are only robust abundance estimates for one of the several "Rias" (Arousa Ria) that are included in the management unit.. Methion y Díaz-López (2018). Ría de Arousa 144 individuals (95% CI :133.1–165.6) winter 2015. Methion y Díaz-López (2018). Ría de Arousa 56 individuals (95% CI:55.2–66.4) summer 2014	Metathion and DÃazo-LÃ³pez (2018). TEP: 0.68 Â±Â 0.12	Metathion and DÃazo-LÃ³pez (2018). SR: 1.0 Â±Â 0.0 for Raia de Arousa		(MÃ©ndez-Fernrandez et al., 2013b	(Méndez-Fernandez et al., 2013b; Méndez-Fernández et al., 2014). CONC-B-OT: Cd 5.7±13.8 μg/g
Related indicator	Marine mammals By catch-	Marine mammals Abundance		MM-DIST_P		Marine mammals By catch- Porcentaje varados	Marine mammals Abundance		Marine mammals_Spatial Distribution	Marine mammals Mercurio	Marine mammals Mercurio	Marine mammals Cadmio	Marine mammals By catch-	Marine mammals Abundance		Marine mammals_ Distribution Pattern		Marine mammals By catch-	Marine mammals By catch- Porcentaje varados	Marine mammals Abundance	Marine mammals Caracteristicas demograficas_ Age distribution	Marine mammals Caracteristicas demograficas_ Annual Gestation Rate	Marine mammals Caracteristicas demograficas_ Life Expectation	Marine mammals Caracteristicas demograficas_ Natural_Mortality Rate	Marine mammals Caracteristicas demograficas_ Size_length	Marine mammals Caracteristicas demograficas_ Sex distribution	Marine mammals_Spatial Distribution	MM-CONT	Marine mammals Annual Mortality Rate	MM_BYC-SP	Marine mammals Abundance	Marine mammals Caracteristicas demograficas_ Age distribution	Marine mammals Caracteristicas demograficas_ Annual Gestation Rate	Marine mammals Caracteristicas demograficas_ Body_Index	Marine mammals Caracteristicas demograficas_ Size_length	Marine mammals Caracteristicas demograficas_ Sex distribution	Marine mammals_Spatial Distribution	Marine mammals_ Habitat Extention	Marine mammals_ Habitat Condition	Marine mammals By catch-	Marine mammals By catch- Porcentaje varados	Marine mammals Abundance	MM_DEM_TEP	Marine mammals Caracteristicas demograficas_ Survival Rate	MM_DIST_R	Marine mammals Mercurio	Marine mammals Cadmio	Marine mammals By catch-	Marine mammals By catch- Porcentaje varados	Marine mammals Abundance	MM_DEM_TEP	Marine mammals Caracteristicas demograficas_ Survival Rate	Marine mammals_ Distribution Pattern	Marine mammals Mercurio	Marine mammals Cadmio
Criteria status	Unknown	Unknown	Unknown	Good	Unknown	Not good	Unknown	Unknown	Good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Good	Unknown	Not good	Not good	Good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Good	Unknown	Not good	Not good	Unknown	Not good	Not good	Not good	Not good	Not good	Unknown	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Unknown	Good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Good	Unknown	Unknown
Description criteria	The GES status of the D1C1 criterion for the UG21-BP atlantic population can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient.	The GES status of the D1C2 criterion for the UG21-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG21-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.		The GES status of the D1C5 criterion for the UG21-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C1 criterion for the UG13-GM atlantic population can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient. In any case, the data available so far suggest that it is NOT IN GES.	The GES status of the D1C2 criterion for the UG13-GM atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG13-GM atlantic population can not be established conclusively because the available information is incomplete / insufficient.		The GES status of the D1C5 criterion for the UG13-GM atlantic populationUG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG13-GM atlantic populationUG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG13-GM atlantic populationUG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	TThe GES status of the D1C1 criterion for the UG16-ZC atlantic population can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient.	The GES status of the D1C2 criterion for the UG16-ZC atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG16-ZC atlantic population can not be established conclusively because the available information is incomplete / insufficient.		The GES status of the D1C5 criterion for the UG16-ZC atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C1 criterion for the UG9-DD atlantic population can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient. In any case, the data available so far suggest that it is NOT IN GES.	The GES status of the D1C1 criterion for the UG9-DD atlantic population can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient. In any case, the data available so far suggest that it is NOT IN GES.	The GES status of the D1C2 criterion for the UG9-DD atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG9-DD atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG9-DD atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG9-DD atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG9-DD atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG9-DD atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG9-DD atlantic population can not be established conclusively because the available information is incomplete / insufficient.		The GES status of the D1C5 criterion for the UG9-DD atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C1 criterion for the UG1-PP Iberian population can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient. In any case, the data available so far suggest that it is NOT IN GES.	The GES status of the D1C1 criterion for the UG1-PP Iberian population can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient. In any case, the data available so far suggest that it is NOT IN GES.	The GES status of the D1C2 criterion for the UG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG1-PP Iberian population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C1 criterion for the UG3-TT northern and northwester continental shelf waters. can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient. In any case, the data available so far suggest that it is NOT IN GES.	The GES status of the D1C1 criterion for the UG3-TT northern and northwester continental shelf waters. can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient. In any case, the data available so far suggest that it is NOT IN GES.	The GES status of the D1C2 criterion for the UG3-TT northern and northwester continental shelf waters can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG3-TT northern and northwester continental shelf waters. can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG3-TT northern and northwester continental shelf waters. can not be established conclusively because the available information is incomplete / insufficient.		The GES status of the D1C5 criterion for the UG3-TT northern and northwester continental shelf waters.can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG3-TT northern and northwester continental shelf waters.can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C1 criterion for the UG2-TT coastal waters South Galicia can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient.	The GES status of the D1C1 criterion for the UG2-TT coastal waters South Galicia can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient.	The GES status of the D1C2 criterion for the UG2-TT coastal waters South Galicia can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG2-TT coastal waters South Galicia can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG2-TT coastal waters South Galicia can not be established conclusively because the available information is incomplete / insufficient.		The GES status of the D1C5 criterion for the UG2-TT coastal waters South Galicia can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG2-TT coastal waters South Galicia can not be established conclusively because the available information is incomplete / insufficient.
Element status	Unknown	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Description element																		Element Source: UG9-DD Stock	Element Source: UG9-DD Stock	Element Source: UG9-DD Stock	Element Source: UG9-DD Stock	Element Source: UG9-DD Stock	Element Source: UG9-DD Stock	Element Source: UG9-DD Stock	Element Source: UG9-DD Stock	Element Source: UG9-DD Stock	Element Source: UG9-DD Stock	Element Source: UG9-DD Stock												Element Source: UG3-TT northern and northwester continental shelf waters.	Element Source: UG3-TT northern and northwester continental shelf waters.	Element Source: UG3-TT northern and northwester continental shelf waters.	Element Source: UG3-TT northern and northwester continental shelf waters.	Element Source: UG3-TT northern and northwester continental shelf waters.	Element Source: UG3-TT northern and northwester continental shelf waters.	Element Source: UG3-TT northern and northwester continental shelf waters.	Element Source: UG3-TT northern and northwester continental shelf waters.
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	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	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	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.	The OOAO method has been applied directly in the case of primary criteria. In the case of secondary criteria, the expert criterion has also been taken into account for integration.
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Assessments period	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017
Related pressures	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Litter in the environment	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Litter in the environment	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Litter in the environment	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Litter in the environment	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	Input of anthropogenic sound (impulsive, continuous) Litter in the environment	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)	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)	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)	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	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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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.12 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-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M	D1-M
Feature	Baleen whales	Baleen whales	Baleen whales	Baleen whales	Baleen whales	Baleen whales	Baleen whales	Baleen whales	Baleen whales	Baleen whales	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans
Element	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Balaenoptera physalus	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Delphinus delphis	Orcinus orca	Orcinus orca	Orcinus orca	Orcinus orca	Orcinus orca	Orcinus orca	Orcinus orca	Orcinus orca	Orcinus orca	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus	Tursiops truncatus
Element code	137091	137091	137091	137091	137091	137091	137091	137091	137091	137091	137094	137094	137094	137094	137094	137094	137094	137094	137094	137094	137102	137102	137102	137102	137102	137102	137102	137102	137102	137111	137111	137111	137111	137111	137111	137111	137111	137111	137111
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/	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/	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/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/
Element 2	UG22-BP Atlanac population	UG22-BP Atlanac population	UG22-BP Atlanac population	UG22-BP Atlanac population	UG22-BP Atlanac population	UG22-BP Atlanac population	UG22-BP Atlanac population	UG22-BP Atlanac population	UG22-BP Atlanac population	UG22-BP Atlanac population	UG10-DD taltantic population	UG10-DD taltantic population	UG10-DD taltantic population	UG10-DD taltantic population	UG10-DD taltantic population	UG10-DD taltantic population	UG10-DD taltantic population	UG10-DD taltantic population	UG10-DD taltantic population	UG10-DD taltantic population										UG4-TT continental shelf gulf of CÃ¡diz	UG4-TT continental shelf gulf of CÃ¡diz	UG4-TT continental shelf gulf of CÃ¡diz	UG4-TT continental shelf gulf of CÃ¡diz	UG4-TT continental shelf gulf of CÃ¡diz	UG4-TT continental shelf gulf of CÃ¡diz	UG4-TT continental shelf gulf of CÃ¡diz	UG4-TT continental shelf gulf of CÃ¡diz	UG4-TT continental shelf gulf of CÃ¡diz	UG4-TT continental shelf gulf of CÃ¡diz
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D1C1	D1C2	D1C3	D1C3	D1C3	D1C3	D1C4	D1C4	D1C4	D1C5	D1C1	D1C2	D1C3	D1C3	D1C3	D1C3	D1C4	D1C4	D1C4	D1C5	D1C1	D1C2	D1C3	D1C3	D1C3	D1C4	D1C4	D1C5	D1C5	D1C1	D1C2	D1C3	D1C3	D1C3	D1C3	D1C4	D1C4	D1C4	D1C5
Parameter	Other	Abundance	Age distribution	Fecundity rate	Sex distribution	Survival rate	Distribution (pattern)	Distribution (range)	Distribution (spatial)	Habitat condition	Other	Abundance	Age distribution	Fecundity rate	Sex distribution	Survival rate	Distribution (pattern)	Distribution (range)	Distribution (spatial)	Other	Other	Abundance	Other	Other	Survival rate	Distribution (pattern)	Distribution (spatial)	Other	Other	Other	Abundance	Age distribution	Fecundity rate	Sex distribution	Survival rate	Distribution (pattern)	Distribution (range)	Distribution (spatial)	Other
Parameter other	Percentage of fin whales stranded with signals compatible with bycatch.										Percentage of stranded common dolphins with signals compatible with bycatch									CONC-B-OT	Percentage of stranded orcas with signals compatible with bycatch		Breeding interval	Grow rate				CONC-B-OT	duration	Percentage of stranded boltenose dolphins with signals compatible with bycatch									CONC-B-OT
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source
Threshold value source other
Value achieved upper	15.4										5.4	51064.0										39.0								6.2
Value achieved lower												3297.0
Value unit	percentage										percentage	(number of) individuals									percentage	(number of) individuals	Other						decibel	percentage
Value unit other																							years
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Deteriorating	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Unknown	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	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 parameter		There is no abundance estimate for this management unit.										Hammond et al. (2017). Continental shelf: Block AA, 18458 individuals (CV: 0.64, 95%IC: 3297-51064) individuals.								Barón et al. (2015). PBDEs = 203; MeO-PBDEs = 225; HBCD = 30 μg/kg lw.		Esteban et al. (2016). 39 individuals identified. This MU has been monitorized since 1999.	non interacting with tuna fishery (NO INT). " (2- NO INT) BI: 7 años	" ""Growth rate (GR)"" , for two different groups of orcas; interacting with tuna fishery (INT) and non interacting with tuna fishery (NO INT). " (INT) GR: 4%. . (2- NO INT) GR: 0%.	interacting with tuna fishery (INT) (1- INT) SUR: 0.991, SE: 0.011. (2-NO INT) SUR: 0.901 SE: 0.050	DIST-P/DIST-S: While orcas are observed in spring over all located in the Gulf of Cadiz (Guinet et al., 2007, Garcia Tiscar, 2009), in summer they are recorded mainly in the Strait of Gibraltar.	DIST-P/DIST-S: While orcas are observed in spring over all located in the Gulf of Cadiz (Guinet et al., 2007, Garcia Tiscar, 2009), in summer they are recorded mainly in the Strait of Gibraltar.	CONC-B-OT: Jepson et al. (2016), PCB: 215.4 μg/kg lw. Desforges et al. (2018), PCB: 500 mg / kg lw.	DUR: Castellot et al. (2012), 112.5Â dB re: 1 Î¼Pa rms, 10-585Â Hz.		There is no abundance estimate for this management unit.								Barón et al. (2015). PBDEs = 813; MeO-PBDEs = 775; HBCD = 51 μg/kg lw. Jepson et al. (2016), The levels of PCBs found in the bottlenose dolphins were much higher than the normal limits of toxicity for the species.
Related indicator	Marine mammals By catch- Porcentaje varados	Marine mammals Abundance									Marine mammals By catch- Porcentaje varados	Marine mammals Abundance								Marine mammals_ Hexabromociclododecano MM-PBDEs MM_MeO-PBDEs	Marine mammals By catch- Porcentaje varados	Marine mammals Abundance	Marine mammals Caracteristicas demograficas_ Body_Index	MM_DE_GR	Marine mammals Caracteristicas demograficas_ Survival Rate	Marine mammals_ Distribution Pattern	Marine mammals_Spatial Distribution	MM-PCB	MM-DUR	Marine mammals By catch- Porcentaje varados	Marine mammals Abundance								Marine mammals_ Hexabromociclododecano Marine mammals_ Polibromodifenil éteres metoxilados Marine mammals_ polibromodifenil éteres
Criteria status	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not good	Good	Not good	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not good
Description criteria	The GES status of the D1C1 criterion for the UG22-BP atlantic population can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient.	The GES status of the D1C2 criterion for the UG22-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG22-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG22-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG22-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG22-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG22-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG22-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG22-BP atlantic population can not be established conclusively because the available information is incomplete / insufficient.	Panicata et al., 2006	The GES status of the D1C1 criterion for the UG10-DD altantic population can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient.	The GES status of the D1C2 criterion for the UG10-DD altantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG10-DD altantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG10-DD altantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG10-DD altantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG10-DD altantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG10-DD altantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG10-DD altantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG10-DD altantic population can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG10-DD altantic population can not be established conclusively because the available information is incomplete / insufficient.		The GES status of the D1C2 criterion for the UG18-OO gulf of Cádiz and contigous waters can not be established conclusively because the available information is incomplete / insufficient.				The GES status of the D1C4 criterion for the UG18-OO gulf of Cádiz and contigous waters can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG18-OO gulf of Cádiz and contigous waters can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG18-OO gulf of Cádiz and contigous waters can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG18-OO gulf of Cádiz and contigous waters can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C1 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information regarding the impact of bycatch is incomplete / insufficient.	The GES status of the D1C2 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C3 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C4 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information is incomplete / insufficient.	The GES status of the D1C5 criterion for the UG4-TT continental shelf gulf of Cádiz can not be established conclusively because the available information is incomplete / insufficient.
Element status	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good
Description element																					Element Source: UG18-OO gulf of Cádiz and contigous waters	Element Source: UG18-OO gulf of Cádiz and contigous waters	Element Source: UG18-OO gulf of Cádiz and contigous waters	Element Source: UG18-OO gulf of Cádiz and contigous waters	Element Source: UG18-OO gulf of Cádiz and contigous waters	Element Source: UG18-OO gulf of Cádiz and contigous waters	Element Source: UG18-OO gulf of Cádiz and contigous waters	Element Source: UG18-OO gulf of Cádiz and contigous waters	Element Source: UG18-OO gulf of Cádiz and contigous waters
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	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	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	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Assessments period	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017	2011-2017
Related pressures	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of nutrients - diffuse sources, point sources, atmospheric deposition	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous)
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	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	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	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