MS/Art8/2018/D1-B/Portugal/NE Atlantic: Macaronesia — Marine Information System for Europe

Member State report / Art8 / 2018 / D1-B / Portugal / NE Atlantic: Macaronesia

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 Birds
Member State	Portugal
Region/subregion	NE Atlantic: Macaronesia
Reported by	DGRM
Report date	2021-03-03
Report access	ART8_GES_PT_setembro2020.xml

Azores Subdivision (AMA-PT-SD-AZO)

Simplified table

GES component	D1-B
Feature	Pelagic-feeding birds																		Surface-feeding birds
Element	Bulweria bulwerii						Calonectris borealis						Puffinus lherminieri						Hydrobates castro						Hydrobates monteiroi						Sterna dougallii						Sterna hirundo
Element code	137193						1348497						212633						A874						A884						137160						137162
Element code source	Species (D1) http://www.marinespecies.org/						Species (D1) http://www.marinespecies.org/						Species (D1) http://www.marinespecies.org/						Species (D1) http://dd.eionet.europa.eu/vocabulary/biodiversity/n2000birds/view						Species (D1) http://dd.eionet.europa.eu/vocabulary/biodiversity/n2000birds/view						Species (D1) http://www.marinespecies.org/						Species (D1) http://www.marinespecies.org/
Element 2
Element 2 code
Element 2 code source
Element source	National						National						National						National						National						National						National
Criterion	D1C1	D1C2	D1C3		D1C4	D1C5	D1C1	D1C2	D1C3		D1C4	D1C5	D1C1	D1C2	D1C3		D1C4	D1C5	D1C1	D1C2	D1C3		D1C4	D1C5	D1C1	D1C2	D1C3		D1C4	D1C5	D1C1	D1C2	D1C3		D1C4	D1C5	D1C1	D1C2	D1C3		D1C4	D1C5
Parameter	Mortality rate / Mortality rate from fishing (F)	Abundance	Fecundity rate	Survival rate	Distribution (range)		Mortality rate / Mortality rate from fishing (F)	Abundance	Fecundity rate	Survival rate	Distribution (range)		Mortality rate / Mortality rate from fishing (F)	Abundance	Fecundity rate	Survival rate	Distribution (range)		Mortality rate / Mortality rate from fishing (F)	Abundance	Fecundity rate	Survival rate	Distribution (range)		Mortality rate / Mortality rate from fishing (F)	Abundance	Fecundity rate	Survival rate	Distribution (range)		Mortality rate / Mortality rate from fishing (F)	Abundance	Fecundity rate	Survival rate	Distribution (range)		Mortality rate / Mortality rate from fishing (F)	Abundance	Fecundity rate	Survival rate	Distribution (range)
Parameter other
Threshold value upper		70.0	45.7	0.9			1.0	188000.0		0.9						0.9						0.9				250.0		0.9						0.9						0.9
Threshold value lower		50.0																								300.0
Threshold qualitative
Threshold value source	Other (specify)	Birds Directive (79/409/EEC)	Other (specify)		Birds Directive (79/409/EEC)		Other (specify)	MS(sub)region	MS(sub)region	Other (specify)	Birds Directive (79/409/EEC)		MS(sub)region	Birds Directive (79/409/EEC)	MS(sub)region				MS(sub)region	Birds Directive (79/409/EEC)	MS(sub)region	Other (specify)	Birds Directive (79/409/EEC)		Other (specify)	Birds Directive (79/409/EEC)		Other (specify)	Birds Directive (79/409/EEC)		Other (specify)	Other (specify)		Other (specify)	Other (specify)		Other (specify)	Other (specify)		Other (specify)	Other (specify)
Threshold value source other	MISIC SEAS II		MISIC SERAS II project				MISIC SEAS II			MISIC SEAS II												MISIC SERAS II project			MISIC SEAS II			MISIC SERAS II project			MISIC SEAS II	MONIAAVES		MISIC SERAS II project	MONIAAVES		MISIC SEAS II	MONIAAVES		MISIC SERAS II project	MONIAAVES
Value achieved upper		70.0	70.0					188000.0						1741.0						740.0						391.0						1068.0						3411.0
Value achieved lower		50.0												895.0						665.0						361.0						535.0						2419.0
Value unit	Other	Other	Other				Other	(number of) individuals					Other	Other					Other	Other					Other	Other					Other	Other					Other	Other
Value unit other	Number of individuals cautioned	Female Breeds	%				Number of individuals cautioned						Number of individuals cautioned	Female Breeds					Number of individuals cautioned	Female Breeds					Number of individuals cautioned	Female Breeds					Number of individuals cautioned	Female Breeds					Number of individuals cautioned	Female Breeds
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Stable	Unknown	Unknown		Unknown		Stable	Unknown	Unknown		Unknown		Stable	Unknown	Unknown		Unknown		Stable	Unknown	Unknown		Unknown		Stable	Unknown	Unknown		Unknown		Stable	Unknown	Unknown		Unknown		Stable	Unknown	Unknown		Unknown
Parameter achieved	Yes	Unknown	Unknown		Unknown		Yes	Unknown	Unknown		Unknown		Yes	Unknown	Unknown		Unknown		Yes	Unknown	Unknown		Unknown		Yes	Unknown	Unknown		Unknown		Yes	Unknown	Unknown		Unknown		Yes	Unknown	Unknown		Unknown
Description parameter	Não se detetou captura acidental no programa de observação de pesca dos Açores - POPA (Cooper et al., 2003). Cooper, J., Baccetti, N., Belda, E. J., Borg, J. J., and Oro, D. Papaconstantinou, C. Sanchez, A. 2003. Seabird mortality from longline fishing in the Mediterranean Sea and Macronesian waters: a review and a way forward. Scientia Marina, 67: 57–64. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Mantém-se a estimativa populacional total dos Açores de cerca de 50-70 casais reprodutores, conforme Monteiro et al. (1999): 50 no ilhéu Vila, em Santa Maria, 0-10 no ilhéu de Baixo e 0-10 no ilhéu da Praia, na Graciosa. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp. Monteiro, L.R., Ramos, J. A., Pereira, J. C., Monteiro, P. R., Feio, R. S.., Thompson, D. R. Bearhop, S., Furness, R. W., Laranjo, M., Hilton, G., Neves, V. C., Groz, M. P. & Thompson, K. R. 1999. Status and distribuition of Fea's Petrel, Bulwer's Petrel, Manx Shearwater, Little Shearwater and Band-rumped Storm-Petrel in the Azores Archipelago. Waterbirds 22: 358-366 Nunes, M. (2008). Bulweria bulwerii. In Equipa Atlas (eds.): Atlas das Aves Nidificantes em Portugal (1999-2005). Pp. 116-117. Instituto de Conservação da Natureza e Biodiversidade, Sociedade Portuguesa para o Estudo das Aves, Parque Natural da Madeira, Secretaria Regional do Ambiente e do Mar. Assírio & Alvim, Lisboa.	The relevant parameter is the breeding success rather than the fertility rate and was only estimated for the Illéu do Vila. This is a colony free colony with an average breeding success from 2002-2012 of 45.7 % (J. Briged, unpublished data), defined as a reference for this colony/species. A ...	A taxa de sobrevivência atual ainda não foi calculada e não existe um valor de referência. Estabeleceu-se um limiar de 0,9 para todas as colónias de aves marinhas da Macaronésia. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	The same known breeding colonies as identified by Monteiro et al. (1999): Vila in Santa Maria, Baixo do magie de Praia na Graciosa. The Azores Azores breeding population is only monitored on the island of Vila, Santa Maria, which houses the largest known population of the archipelago and where t...		MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	The total population estimate for the Azores of around 188 000 breeding pairs is maintained, according to Monteiro et al. (1999) and Bolton (2011). Counts were made in some nesting colonies in the research work of the marine bird group of the University of the Azores and the SEAS project, bu...	The breeding success on Corvo island has been estimated at 39 % between 2009 and 2011 (Hervíos et al., 2013). The current breeding success (2015-2018, SPEA, unpublished data) is also 39 %. A breeding success of 81.5 % (2018) based on the monitoring of the 37 selected nests was calc...	A taxa de sobrevivência atual ainda não foi calculada. O valor de referência da taxa de sobrevivência foi estabelecido utilizando dados compilados entre 2002 e 2008, por Fontaine et al. (2011) (Taxa de sobrevivência = 0,934). Estabeleceu-se um limiar de 0,9 para todas as colónias de aves marinhas da Macaronésia. Fontaine, R., Gimenez, O. & Bried, J. 2011. The impact of introduced predators, lightinduced mortality of fledglings and poaching on the dynamics of the Cory's Shearwater (Calonectris diomedea) population from the Azores, northeastern subtropical Atlantic. Biological Conservation 144: 1998-2011.; MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	As colónias nidificantes de cagarro distribuem-se ao longo da costa das ilhas e nos ilhéus por todo o Arquipélago dos Açores. Bolton, M. (2001a). Census of Cory's shearwaters Calonectris diomedea in the Azores archipelago 2001. Final Report. University of the Azores. Magalhães MC 2008. Calonectris diomedea Cagarra In Atlas das Aves Nidificantes em Portugal (1999-2005) (Equipa Atlas eds.). Instituto da Conservação da Natureza, Sociedade Portuguesa para o Estudo das Aves, Parque Natural da Madeira e Secretaria Regional do Ambiente e do Mar. Assírio & Alvim. Lisboa. Monteiro LR, JA Ramos, RW Furness. 1996. Past and Present Status and Conservation of the Seabirds Breeding in the Azores Archipelago. Biological Conservation. 78, 319 – 328. Paiva VH, Geraldes P, Ramírez I, Meirinho A, Garthe S, Ramos JA (2010) Oceanographic characteristics of areas used by Cory’s shearwaters during short and long foraging trips in the North Atlantic. Mar Biol 157:1385−1399		Não se detetou captura acidental no programa de observação de pesca dos Açores - POPA (Cooper et al., 2003). Cooper, J., Baccetti, N., Belda, E. J., Borg, J. J., and Oro, D. Papaconstantinou, C. Sanchez, A. 2003. Seabird mortality from longline fishing in the Mediterranean Sea and Macronesian waters: a review and a way forward. Scientia Marina, 67: 57–64. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Alvim, Lisbon.	O parâmetro em causa é o sucesso reprodutor e não a taxa de fecundidade e foi apenas estimado para as colónias do Ilhéu da Praia, Graciosa (64%) e do Ilhéu da Vila, Santa Maria (50%), durante o MISTIC SEAS II. Estes valores foram utilizados como o valor de referência para futuras avaliações. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	A taxa de sobrevivência atual ainda não foi calculada e não existe um valor de referência. O valor de referência de taxa de sobrevivência foi estabelecido utilizando dados recolhidos entre 1998 e 2005 por Precheur et al. (2016) (Taxa de sobrevivência = 0,943). Estabeleceu-se um limiar de 0,9 para todas as colónias de aves marinhas da Macaronésia. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.			Não se detetou captura acidental no POPA (Cooper et al., 2003, MISTIC SEAS II Consortium, 2018). MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Roughhead grenadier J.P. (2008). Oceanodroma castro. In (eds.): Atlas of Birds Nirentes in Portugal (1999-2005). PP 126	The parameter concerned is the breeding success rather than the fertility rate and was only estimated for the colonies of the Ihoral province of Praia, Graciosa and Illéda Vila, Santa Maria. In the island of Vila, breeding success was estimated at 39.7 % between 2002 and 2012 (J. Briged, unp...	Estabeleceu-se um limiar de 0,9 para todas as colónias de aves marinhas da Macaronésia. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Monteiro et al. (1999) estimated 8 colonies in the Azores. The population size has been estimated during the 90s between 665 and 740 breeding pairs, of which 440-480 are located on the island of Graciosa (200 on the island of Praia, 200 on the Baixa island, 40-80 on the island of Ponta do Barca ?...		MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Bolton et al., 2008)	In Praia, the breeding success was about 41 % in natural nests and 46 % in artificial nests between 2000-2012 (on average, except for 2002, Brited and Neves, 2015). Neves and collaborators (W. Schäfer, T. Karwinkel, L. Gomes, T. Châtelauron, J. Taylor-Bruce and M. AUSTAD, MARE ? UID/MAR...	A taxa de sobrevivência atual ainda não foi calculada, mas o valor de referência de 0,97 calculada por Robert et al. (2012) foi utilizado. Estabeleceu-se um limiar de 0,9 para todas as colónias de aves marinhas da Macaronésia. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	O painho-de-monteiro tem uma população pequena e nidificação restrita a cinco colónias conhecidas: Ilhéu da Praia, Ilhéu de Baixo e Ponta da Barca - ilhéu da Baleia (Graciosa); ilhéu Sentado, Alagoa (Flores) e Ponta do Marco (Corvo). Nos trabalhos do MISTIC SEAS II confirmou-se a nidificação no Ilhéu Sentado, Alagoa, Flores Bolton M., Smith A. L., Gómez-diaz D., Friesen V., Medeiros R., Bried J., Roscales J. L., Furness R. W. (2008) Monteiro's Storm Petrel Oceanodroma monteiroi: a new species from the Azores. Ibis 150, 717-727. Bried, J. & Neves, V.C. 2015. Habitat restoration on Praia Islet, Azores Archipelago, proved successful for seabirds, but new threats have emerged. Airo 23: 25-35. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp. Monteiro L.R., Ramos J.A., Pereira J. C.,Monteiro P. R., Feio R. S., Thompson D. R.,Bearhop S., Furness R. W., Laranjo M., Hilton G., Neves V. C., Groz M. P., and Thompson K.R. (1999).Status and Distribuition of Fea's Petrel, Bulwer's Petrel, Manx Shearwater, and Band-Rumped Storm Petrel in the Azores Archipelago. Waterbirds 22, 358-366. Oliveira, N., Aguiar, L., Barros, N., Bried, J., Carmo, V., Carvalho, A., Cepêda, H., Costa, L., Faustino, L., Lourenço, J., Magalhães, M., Melo, C., Neves, V., Picanço, C., Picanço, M., Paiva, V., Pipa, T., Ramos, J., Raposo, P., Serba, S., Silva, C., Tarzia, M., Teixeira, J., Teodósio, J. & Andrade, J. 2016. Status Report for Monteiro’s Storm-petrel Hydrobates monteiroi. Report of the Action A10, Project LIFE EuroSAP. Sociedade Portuguesa para o Estudo das Aves, Lisboa. Ramírez, J. 2017. Estimación de la densidad del Paiño de Monteiro (Hydrobates monteiroi) mediante bioacústica. Universidad de Vigo.			The data were collected in the framework of the Garajaus Census carried out by the University of the Azores (V. Neves) and DRAMs (MSFD Monitoring Programme ? MONIAVES). Population estimates of this species show interyearly fluctuations, such as spatial distribution of colonies, and there are hist...	Em 2014, a média de posturas para o garajau-rosado foi de 1,4 (n=573) e em 2015 foi de 1,3 ovos por ninho (n=659). Neves, V. 2014. Azores Tern Census Report 2014. University of the Azores, Department of Oceanography & Fisheries. Arquivos do DOP, Série Estudos nº2/2014. Neves, V. 2015. Azores Tern Census Report 2015. University of the Azores, Department of Oceanography & Fisheries. Arquivos do DOP, Série Estudos nº1/2015.	A taxa de sobrevivência atual ainda não foi calculada e não existe um valor de referência para os Açores. Estabeleceu-se um limiar de 0,9 para todas as colónias de aves marinhas da Macaronésia. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Fisheries. Archives of the PDO, Series of studies No 5/2012. Neves, V. 2014. Azores Census Report 2014. University of the Azres, Department of Oceanography			Fisheries. Archives of the PDO, Series of studies No 1/2015. DRAM 2016. Census of Garajaus (Sterna spp.) in the subdivision of the Portuguese EEZ of the Autonomous Region of the Azores ? Report 2016. Implementation of the Marine Strategy Framework Directive. MOA01-III ? MONIAVES ? monitoring pr...	Em 2014 a média de posturas para o garajau-comum foi de 2,2 (n=573) e em 2015 foi de 2,1 ovos por ninho (n=659). Neves, V. 2014. Azores Tern Census Report 2014. University of the Azores, Department of Oceanography & Fisheries. Arquivos do DOP, Série Estudos nº2/2014. Neves, V. 2015. Azores Tern Census Report 2015. University of the Azores, Department of Oceanography & Fisheries. Arquivos do DOP, Série Estudos nº1/2015.	A taxa de sobrevivência atual ainda não foi calculada e não existe um valor de referência para os Açores. Estabeleceu-se um limiar de 0,9 para todas as colónias de aves marinhas da Macaronésia. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Fisheries. Archives of the PDO, Series of studies No 5/2012. Neves, V. 2014. Azores Census Report 2014. University of the Azres, Department of Oceanography
Related indicator	SeaBirdsBycatch	SeaBirdsAbundanceMONIAVES SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsDistributionRange		SeaBirdsBycatch	SeaBirdsAbundanceMONIAVES SeaBirdsAbundanceRaftCount SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsDistributionRange		SeaBirdsBycatch	SeaBirdsAbundanceMONIAVES SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsDistributionRange		SeaBirdsBycatch	SeaBirdsAbundanceMONIAVES SeaBirdsAbundanceCallRate SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsDistributionRange		SeaBirdsBycatch	SeaBirdsAbundanceMONIAVES SeaBirdsAbundanceCallRate SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsDistributionRange		SeaBirdsBycatch	SeaBirdsAbundanceMONIAVES	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsAbundanceMONIAVES		SeaBirdsBycatch	SeaBirdsAbundanceMONIAVES	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsAbundanceMONIAVES
Criteria status	Good	Unknown	Unknown		Unknown	Unknown	Good	Unknown	Unknown		Unknown	Unknown	Good	Unknown	Unknown		Unknown	Unknown	Good	Unknown	Unknown		Unknown	Unknown	Good	Unknown	Unknown		Unknown	Unknown	Good	Unknown	Unknown		Unknown	Unknown	Good	Unknown	Unknown		Unknown	Unknown
Description criteria	Não se detetou captura acidental no programa de observação de pesca dos Açores - POPA (Cooper et al., 2003). No entanto, recomenda-se monitorização futura para suprir as lacunas de conhecimento nas artes de pesca que não são abrangidas pelo programa de monitorização. Cooper, J., Baccetti, N., Belda, E. J., Borg, J. J., and Oro, D. Papaconstantinou, C. Sanchez, A. 2003. Seabird mortality from longline fishing in the Mediterranean Sea and Macronesian waters: a review and a way forward. Scientia Marina, 67: 57–64. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Alvim, Lisbon.	Os parâmetros demográficos foram estimados através das metodologias estabelecidas pelo projeto MISTIC SEAS II (ver Macaronesian Roof Report) e apenas para o ilhéu da Vila, em Santa Maria. O BEA desta UG só se pode avaliar com rigor com dados de monitorização de, pelo menos, 6 épocas de nidificação. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.		There is no updated stock census of Procellariformes since the work of Monteiro et al. (1999) at regional level (all AAR) to measure the actual distribution area of the various species and total population and to assess GES.	Habitat for the species is a secondary criterion for seabirds (Commission Decision (EU) 2017/848, 2017). No information or monitoring schemes are available on the habitat of seabirds. This criterion refers to the state of the marine habitat. Seabirds, large migratory birds, may experience pressur...	Uma revisão dos eventos de captura acidental de aves marinhas até ao ano 2000, reporta que apenas um indivíduo, presumivelmente um cagarro (Calonectris borealis), foi encontrado morto num palangre demersal nos Açores (Cooper et al., 2003, MISTIC SEAS II Consortium, 2018). O valor atual para este critério neste ciclo é de 0 indivíduos (2018, POPA; MISTIC SEAS II). Cooper, J., Baccetti, N., Belda, E. J., Borg, J. J., and Oro, D. Papaconstantinou, C. Sanchez, A. 2003. Seabird mortality from longline fishing in the Mediterranean Sea and Macronesian waters: a review and a way forward. Scientia Marina, 67: 57–64. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	The population of the Azores is estimated to account for around 75 % of the world breeding population (BirdLife International, 2018). The total population estimate of Monteiro et al. (1999) was 403.920 individuals in 1996 in the Azores. Bolton (2001a), on the basis of the methodology develo...	Capelhos and Morro de Castelo Branco, Faial. JCC II consortium (2018) Macaronesian Roof Report (TRWP2) ? Applying a sub-regional close and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 ? Towards a co-beneficiary ...	Os parâmetros demográficos foram estimados através das metodologias estabelecidas pelo projeto MISTIC SEAS II (ver Macaronesian Roof Report) para efeitos de avaliação no próximo ciclo, para as seguintes colónias (unidades de gestão): ilha do Corvo; Ilhéu de Vila Franca do Campo, São Miguel; Monte e Mistério da Prainha, Pico; Ilhéu da Praia, Graciosa; Ilhéu da Vila, Santa Maria; Capelinhos e Morro de Castelo Branco, Faial. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	There is no updated stock census of Procellariformes since the work of Monteiro et al. (1999) at regional level (all AAR) to measure the actual distribution area of the various species and total population and to assess GES. The garden centres on the coast of all the islands of the Azores, mai...	Habitat for the species is a secondary criterion for seabirds (Commission Decision (EU) 2017/848, 2017). No information or monitoring schemes are available on the habitat of seabirds. This criterion refers to the state of the marine habitat. Seabirds, large migratory birds, may experience pressur...	Não se detetou captura acidental no programa de observação de pesca dos Açores - POPA (Cooper et al., 2003). Cooper, J., Baccetti, N., Belda, E. J., Borg, J. J., and Oro, D. Papaconstantinou, C. Sanchez, A. 2003. Seabird mortality from longline fishing in the Mediterranean Sea and Macronesian waters: a review and a way forward. Scientia Marina, 67: 57–64. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Population estimates of this species were made in the AAR mainly in the 1996s and 1997s and occasional listening was carried out in the following years, and the nesting population was estimated through night taps following the Monteiro et al. method (1999), with known colonies on islets and on th...	The demographic parameters have been estimated using the methodologies established by the MISTIC SEAS project (see Macaronesian Roof Report) for the colonies of the Ilhéu da Praia, Graciosa and Ilhéu da Vila, Santa Maria. The GES of these colonies can only be accurately assessed with monitoring d...	Os parâmetros demográficos foram estimados através das metodologias estabelecidas pelo projeto MISTIC SEAS (ver Macaronesian Roof Report) para as colónias do Ilhéu da Praia, Graciosa e Ilhéu da Vila, Santa Maria. O BEA destas colónias só se pode avaliar com rigor com dados de monitorização de, pelo menos, 6 épocas de nidificação. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Alvim, Lisbon.	O habitat para a espécie é um critério secundário para aves marinhas (Decisão 2017/848/EU, 2017 da Comissão). Não se dispõe de informação nem de esquemas de monitorização sobre o habitat das aves marinhas. Este critério refere-se ao estado do habitat marinho. As aves marinhas, grandes migratórias, podem sofrer pressões nas suas zonas de alimentação e / ou de invernada não abrangidas nos programas de monitorização atuais devido à falta de conhecimento sobre a distribuição no mar de indivíduos de algumas espécies, sexo e classes etárias e desafios de monitorização (Lewison et al., 2012). MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Não se detetou captura acidental no programa de observação de pesca dos Açores - POPA (Cooper et al., 2003). No entanto, recomenda-se monitorização futura para suprir as lacunas de conhecimento nas artes de pesca que não são abrangidas pelo programa de monitorização. Cooper, J., Baccetti, N., Belda, E. J., Borg, J. J., and Oro, D. Papaconstantinou, C. Sanchez, A. 2003. Seabird mortality from longline fishing in the Mediterranean Sea and Macronesian waters: a review and a way forward. Scientia Marina, 67: 57–64. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Refined and Neves, 2015). There is no data on the total population, however the regular monitoring carried out in the 3 main colonies (Ihaia da Praia, Baixo and Vila) shows that the population in these colonies is stable. In 2017 SPEA registered a new nesting colony in the SSPA project in (Flores...	Os parâmetros demográficos foram analisados através das metodologias estabelecidas pelo projeto MISTIC SEAS II (ver Macaronesian Roof Report) para as colónias do Ilhéu da Praia, Graciosa e Ilhéu da Vila, Santa Maria. O BEA só se pode avaliar com rigor com dados de monitorização de, pelo menos, 6 ...	Os parâmetros demográficos foram analisados através das metodologias estabelecidas pelo projeto MISTIC SEAS II (ver Macaronesian Roof Report) para as colónias do Ilhéu da Praia, Graciosa e Ilhéu da Vila, Santa Maria. O BEA só se pode avaliar com rigor com dados de monitorização de, pelo menos, 6 épocas de nidificação. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	There is no updated stock census of Procellariformes since the work of Monteiro et al. (1999) at regional level (all AAR) to measure the actual distribution area of the various species and total population and to assess GES.	Habitat for the species is a secondary criterion for seabirds (Commission Decision (EU) 2017/848, 2017). No information or monitoring schemes are available on the habitat of seabirds. This criterion refers to the state of the marine habitat. Seabirds, large migratory birds, may experience pressur...	Não se detetou captura acidental no programa de observação de pesca dos Açores - POPA (Cooper et al., 2003). No entanto, recomenda-se monitorização futura para suprir as lacunas de conhecimento nas artes de pesca que não são abrangidas pelo programa de monitorização. Cooper, J., Baccetti, N., Belda, E. J., Borg, J. J., and Oro, D. Papaconstantinou, C. Sanchez, A. 2003. Seabird mortality from longline fishing in the Mediterranean Sea and Macronesian waters: a review and a way forward. Scientia Marina, 67: 57–64. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	O painho-de-monteiro é uma espécie endémica dos Açores, com uma população pequena (361-391 casais reprodutores) e nidificação restrita a cinco colónias, distribuídas pelas ilhas Graciosa, Flores e Corvo. Bolton M., Smith A. L., Gómez-diaz D., Friesen V., Medeiros R., Bried J., Roscales J. L., Furness R. W. (2008) Monteiro's Storm Petrel Oceanodroma monteiroi: a new species from the Azores. Ibis 150, 717-727. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp. Monteiro L.R., Ramos J.A., Pereira J. C.,Monteiro P. R., Feio R. S., Thompson D. R.,Bearhop S., Furness R. W., Laranjo M., Hilton G., Neves V. C., Groz M. P., and Thompson K.R. (1999). Status and Distribuition of Fea's Petrel, Bulwer's Petrel, Manx Shearwater, and Band-Rumped Storm Petrel in the Azores Archipelago. Waterbirds 22, 358-366. Oliveira, N., Aguiar, L., Barros, N., Bried, J., Carmo, V., Carvalho, A., Cepêda, H., Costa, L., Faustino, L., Lourenço, J., Magalhães, M., Melo, C., Neves, V., Picanço, C., Picanço, M., Paiva, V., Pipa, T., Ramos, J., Raposo, P., Serba, S., Silva, C., Tarzia, M., Teixeira, J., Teodósio, J. & Andrade, J. 2016. Status Report for Monteiro’s Storm-petrel Hydrobates monteiroi. Report of the Action A10, Project LIFE EuroSAP. Sociedade Portuguesa para o Estudo das Aves, Lisboa. Ramírez, J. 2017. Estimación de la densidad del Paiño de Monteiro (Hydrobates monteiroi) mediante bioacústica. Universidad de Vigo.	O BEA só se pode avaliar com rigor com dados de monitorização de, pelo menos, 6 épocas de nidificação. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.		There is no updated stock census of Procellariformes since the work of Monteiro et al. (1999) at regional level (all AAR) to measure the actual distribution area of the various species and total population and to assess GES.	Habitat for the species is a secondary criterion for seabirds (Commission Decision (EU) 2017/848, 2017). No information or monitoring schemes are available on the habitat of seabirds. This criterion refers to the state of the marine habitat. Seabirds, large migratory birds, may experience pressur...	Não se detetou captura acidental no programa de observação de pesca dos Açores - POPA (Cooper et al., 2003). Cooper, J., Baccetti, N., Belda, E. J., Borg, J. J., and Oro, D. Papaconstantinou, C. Sanchez, A. 2003. Seabird mortality from longline fishing in the Mediterranean Sea and Macronesian waters: a review and a way forward. Scientia Marina, 67: 57–64. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.		There are no current studies of demographic parameters with regional coverage to assess this criterion with confidence.		The population estimates of the Garajaus (Charadriiformes) show noticeable inter-annual fluctuations observed in the annual censuses that make it difficult to assess their status. Only with long data series will it be possible to understand whether the observed changes between the different sampl...	Habitat for the species is a secondary criterion for seabirds (Commission Decision (EU) 2017/848, 2017). No information or monitoring schemes are available on the habitat of seabirds. This criterion refers to the state of the marine habitat. Seabirds, large migratory birds, may experience pressur...	Não se detetou captura acidental no programa de observação de pesca dos Açores - POPA (Cooper et al., 2003). Cooper, J., Baccetti, N., Belda, E. J., Borg, J. J., and Oro, D. Papaconstantinou, C. Sanchez, A. 2003. Seabird mortality from longline fishing in the Mediterranean Sea and Macronesian waters: a review and a way forward. Scientia Marina, 67: 57–64. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.		There are no current studies of demographic parameters with regional coverage to assess this criterion with confidence.		The population estimates of the Garajaus (Charadriiformes) show noticeable inter-annual fluctuations observed in the annual censuses that make it difficult to assess their status. Only with long data series will it be possible to understand whether the observed changes between the different sampl...	Habitat for the species is a secondary criterion for seabirds (Commission Decision (EU) 2017/848, 2017). No information or monitoring schemes are available on the habitat of seabirds. This criterion refers to the state of the marine habitat. Seabirds, large migratory birds, may experience pressur...
Element status	Unknown						Unknown						Unknown						Unknown						Unknown						Unknown						Unknown
Description element	Os resultados preliminares do projeto MISTIC SEAS revelam que esta espécie se encontra em BEA nos Açores para o critério D1C1, com uma aparente tendência estável. Os restantes critérios têm um BEA desconhecido, pelo que a avaliação geral da espécie é também desconhecida. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Os resultados preliminares do projeto MISTIC SEAS revelam que esta espécie se encontra em BEA nos Açores para o critério D1C1, com uma aparente tendência estável. Os restantes critérios têm um BEA desconhecido, pelo que a avaliação geral da espécie é também desconhecida. MISTIC SEAS II consorti...	Os resultados preliminares do projeto MISTIC SEAS revelam que esta espécie se encontra em BEA nos Açores para o critério D1C1, com uma aparente tendência estável. Os restantes critérios têm um BEA desconhecido, pelo que a avaliação geral da espécie é também desconhecida. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.	Os resultados preliminares do projeto MISTIC SEAS revelam que esta espécie se encontra em BEA nos Açores para o critério D1C1, com uma aparente tendência estável. Os restantes critérios têm um BEA desconhecido, pelo que a avaliação geral da espécie é também desconhecida. MISTIC SEAS II consorti...	Os resultados preliminares do projeto MISTIC SEAS revelam que esta espécie se encontra em BEA nos Açores para o critério D1C1, com uma aparente tendência estável. Os restantes critérios têm um BEA desconhecido, pelo que a avaliação geral da espécie é também desconhecida. MISTIC SEAS II consortium (2018) Macaronesian Roof Report (TRWP2) - Applying a sub-regional coherent and coordinated approach to the monitoring and assessment of marine biodiversity in Macaronesia for the second cycle of the MSFD. WP2 - Towards a coherent update of initial assessment, GES and targets, Task 2.1. Update of the Initial Assessment and Task 2.2. Finding common GES definition and Environmental Targets for the Macaronesia GA No 11.0661/2017/750679/SUB/ENV.C2., Brussels, 132pp.		The preliminary results of the MISTIC SEAS project show that this species is in GES in the Azores for D1C1, with an apparent stable trend. The remaining criteria have unknown GES, so the overall assessment of the species is also unknown.						The preliminary results of the MISTIC SEAS project show that this species is in GES in the Azores for D1C1, with an apparent stable trend. The remaining criteria have unknown GES, so the overall assessment of the species is also unknown.						The preliminary results of the MISTIC SEAS project show that this species is in GES in the Azores for D1C1, with an apparent stable trend. The remaining criteria have unknown GES, so the overall assessment of the species is also unknown.						The preliminary results of the MISTIC SEAS project show that this species is in GES in the Azores for D1C1, with an apparent stable trend. The remaining criteria have unknown GES, so the overall assessment of the species is also unknown.						The preliminary results of the MISTIC SEAS project show that this species is in GES in the Azores for D1C1, with an apparent stable trend. The remaining criteria have unknown GES, so the overall assessment of the species is also unknown.						The preliminary results of the MISTIC SEAS project show that this species is in GES in the Azores for D1C1, with an apparent stable trend. The remaining criteria have unknown GES, so the overall assessment of the species is also unknown.
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria	For assessment and integration of environmental status it is essential to collect a wider/diverse set of data, filling gaps for a precision assessment. the suggested integration rule OOAO (WG BEA, 2017) could offer a reliable and robust integration method if the status of each element, criterion, indicator could be assessed with a very high degree of confidence, this is rarely the case.																		For assessment and integration of environmental status it is essential to collect a wider/diverse set of data, filling gaps for a precision assessment. the suggested integration rule OOAO (WG BEA, 2017) could offer a reliable and robust integration method if the status of each element, criterion, indicator could be assessed with a very high degree of confidence, this is rarely the case.
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	Unknown																		Unknown
Description overall status	All marine bird species appear to be in GES for D1C1, for the assessed fisheries (MISIC SEAS II Consortium, 2018). However, it is necessary to assess the fishing gear not covered by the current monitoring programmes, so the confidence level of this assessment is low. D1C2 and D1C4: There is no up...																		All marine bird species appear to be in GES for D1C1, for the assessed fisheries (MISIC SEAS II Consortium, 2018). However, it is necessary to assess the fishing gear not covered by the current monitoring programmes, so the confidence level of this assessment is low. D1C2 and D1C4: There is no up...
Assessments period	2012-2018																		2012-2018
Related pressures	Input of litter (solid waste matter, including micro-sized litter) Input of other forms of energy (including electromagnetic fields, light and heat) Input or spread of non-indigenous species																		Disturbance of species (e.g. where they breed, rest and feed) due to human presence Input of litter (solid waste matter, including micro-sized litter) Input of other forms of energy (including electromagnetic fields, light and heat) Input or spread of non-indigenous species
Related targets

Madeira subdivision (AMA-PT-SD-MAD)

Simplified table

GES component	D1-B
Feature	Pelagic-feeding birds																				Surface-feeding birds
Element	Bulweria bulwerii				Calonectris borealis				Pterodroma deserta				Pterodroma madeira				Puffinus lherminieri				Hydrobates castro	Pelagodroma marina
Element code	137193				226024				759338				137198				212633				137193	212700
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/
Element 2
Element 2 code
Element 2 code source
Element source	MS in (sub)region				MS in (sub)region				MS in (sub)region				MS in (sub)region				MS in (sub)region				MS in (sub)region	MS in (sub)region
Criterion	D1C2	D1C3		D1C4	D1C2	D1C3		D1C4	D1C2	D1C3		D1C4	D1C2	D1C3		D1C4	D1C2	D1C3		D1C4	D1C4	D1C2	D1C3		D1C4
Parameter	Abundance	Other	Survival rate	Distribution (range)	Abundance	Other	Survival rate	Distribution (range)	Abundance	Other	Survival rate	Distribution (range)	Abundance	Other	Survival rate	Distribution (range)	Abundance	Other	Survival rate	Distribution (range)	Distribution (range)	Abundance	Other	Survival rate	Distribution (range)
Parameter other		Breeding roots				Breeding roots				Breeding roots				Breeding roots				Breeding roots					Breeding roots
Threshold value upper			0.9				0.9				0.9				0.9				0.9					0.9
Threshold value lower
Threshold qualitative
Threshold value source			MS(sub)region				MS(sub)region				MS(sub)region				MS(sub)region				MS(sub)region					MS(sub)region
Threshold value source other
Value achieved upper															0.6
Value achieved lower
Value unit	Other	percentage	Other		Other	percentage	Other		Other		Other			percentage	Other		Other	percentage	Other		Other			Other
Value unit other	Percentage		Decimal		Percentage		Decimal		Percentage		Decimal				Decimal		Percentage		Decimal		Number of colonies			Decimal
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Improving	Deteriorating	Unknown	Unknown	Unknown	Unknown		Unknown	Unknown	Unknown		Unknown	Unknown	Unknown		Unknown	Unknown	Unknown		Unknown	Unknown	Unknown	Unknown		Unknown
Parameter achieved	Not assessed	Not assessed		Unknown	Not assessed	Not assessed	Unknown	Unknown	Unknown	Unknown	Not assessed	Unknown	Not assessed	Unknown	Not assessed	Not assessed	Not assessed	Unknown	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed		Unknown
Description parameter	Regular monitoring of the black ma- is sparse in the Great. The latest estimates suggest a population of 5000 breeding pairs (Zino and biscuit, 1994) whose methodology is not comparable to that laid down in MSII and will therefore not be used as a benchmark. The abundance of blackgrass has been e...	The breeding success of the black lavender has been evaluated with standardised parameters and agreed for Macaronesia, 71.79 % for 2017 and 28.57 % for 2018. The average of the two years is 50.18 %.	The current survival rate has not been calculated and there is no reference value for this colony. A threshold of 0.9 for all seabird colonies in Macaronesia has been established. However, 40 birds were ringed during 2018.	There is not yet an assessment of BEA available for the whole colony	The size of the garga was valued with the standardised methodology agreed for Macaronesia and was 96.70 % for 2017 and 67.88 % for 2018. The average of the two years is 87.99 %.	Breeding success was 52 % for the 1992-1999 (Mougin 2001). Breeding success was assessed using the standardised methodology for Macaronesia, 96.59 % for 2017 and 80.58 % for 2018. The average of the two years is 88.59 %.	current survival rate not yet calculated (155 ringed birds in 2018) and there is no reference value for this colony. A threshold of 0.9 for all seabird colonies in Macaronesia has been established.	Carga distribution area not yet evaluated in Madeira	A total of 160-180 breeding pairs have been estimated in the colony (Jesus et al., 2009). However, the size of the freiaggio charter has not yet been assessed with the current method set out in Madeira. Therefore, no assessment can be carried out for this colony.	The breeding success of the river chartering has not yet been assessed in Madeira.	The survival rate has not yet been calculated and there is no reference value for this colony. A threshold of 0.9 for all sea bird colonies in Macaronesia has been established	The distribution of the chartering round has not yet been assessed in Madeira.	The size of the population is considered to range from 30-40 breeding pairs to 65-80 CR, estimated as part of the project LIFE00 NAT/P/007097 for the conservation of Madeira through the restoration of their habitat in 2001/2006 coordinated by IFCN-RAM. However, the size of the Madeira freia-Madei...	No SR values available for this species. Therefore it is not yet possible to establish a benchmark for using An assessment under this criterion	The current survival rate has been calculated with a reference value for this colony. A threshold of 0.9 for all seabird colonies in Macaronesia has been established.		The size of the painter was valued using the standardised methodology and agreed for Macaronesia. The size was calculated only for 2018 and was 26.53 %.	The breeding success of the painter was estimated at 80 % in 2011 (Fagundes et al., 2016). SR is now calculated only for the year 2018 and is 42.31 %.	The current survival rate has not yet been calculated and there is no reference value for this colony, with 15 birds ringed. A threshold of 0.9 for all seabird colonies in Macaronesia has been established.	Distribution of the Pintainho was not assessed in Madeira		Estimate only for the Small and Off Charity of Out (Caty et al., 2010).
Related indicator	SeaBirdsAbundanceNestCount	SeaBirdsSurvivalRate		SeaBirdsDistributionRange	SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsDistributionRange	SeaBirdsAbundanceCallRate SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsDistributionRange	SeaBirdsAbundanceCallRate SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsDistributionRange	SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	SeaBirdsSurvivalRate	SeaBirdsDistributionRange	SeaBirdsDistributionRange	SeaBirdsAbundanceNestCount	SeaBirdsBreedingSuccess	AMA-DEM-SR	SeaBirdsDistributionRange
Criteria status	Not assessed	Not assessed		Not assessed	Not assessed	Not assessed		Not assessed	Not assessed	Not assessed		Not assessed	Not assessed	Not assessed		Good	Not assessed	Not assessed		Not assessed	Not assessed	Not assessed	Not assessed		Not assessed
Description criteria	There is not yet an assessment of the BEA available for the whole colony.	There is still no assessment of BEA available for all colóni		The distribution area of the black alma-is not assessed for the subdivision of Madeira	The overall assessment of GES for this colony is not yet available			Carga distribution area not yet evaluated in Madeira	There is not yet an assessment of BEA available for the whole colony	There is not yet an assessment of BEA available for the whole colony		The distribution of the ?hornão? has not yet been assessed in the Madeira.	An assessment of GES for the whole colony is not yet available	An assessment of GES for the whole colony is not yet available		The breeding area is restricted to the central mountains of Madeira (Zino et al., 1995), known as the ?Eastern massif?, a Special Protection Area (SPA). Therefore, only one known colony of this species is currently maintained and indicates good environmental status for this criterion.				Distribution of the Pintainho was not assessed in Madeira	At least two colonies are described in Madeira to This species (Atlas Team, 2008b), but the evaluation of its current distribution is not has been carried out	Calcamar abundance has not yet been assessed with standardised methodology agreed for Macaronesia	The breeding success of this colony has not yet been calculated with the standardised methodology agreed for Macaronesia.		The extension of draughts has not yet been assessed in Madeira.
Element status	Not assessed				Not assessed				Not assessed				Not assessed				Not assessed				Not assessed	Not assessed
Description element	There is not yet an assessment of BEA available for the whole colony				The overall assessment of GES for this colony is not yet available				There is not yet an assessment of BEA available for the whole colony				An assessment of GES for the whole colony is not yet available				An assessment of GES for this colony is not yet available					Still there is an GES assessment available for the whole colony
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	Not assessed																				Not assessed
Description overall status	However, there are gaps in the information needed for a rigorous assessment. In the context of MISICT SEAS I, the group of marine birds followed a stop light methodology to find common bases between the archipelagos and to determine indicators as well as the feasibility of the proposed monitoring methods																				However, there are gaps in the information needed for a rigorous assessment. In the context of MISICT SEAS I, the group of marine birds followed a stop light methodology to find common bases between the archipelagos and to determine indicators as well as the feasibility of the proposed monitoring methods
Assessments period	2014-2018																				2014-2018
Related pressures	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of other forms of energy (including electromagnetic fields, light and heat) Input or spread of non-indigenous species Litter and micro-litter in species																				Disturbance of species (e.g. where they breed, rest and feed) due to human presence Input of other forms of energy (including electromagnetic fields, light and heat) Input or spread of non-indigenous species Litter and micro-litter in species
Related targets	AMAPT-T003-D1MAD AMAPT-T005-D1MAD AMAPT-T006-D1MAD AMAPT-T007-D1MAD AMAPT-T009-D1MAD AMAPT-T011-D1MAD AMAPT-T012-D1MAD AMAPT-T013-D1MAD AMAPT-T014-D1MAD Diretiva Aves Diretiva Habitats Meta DQEM BEA																				AMAPT-T003-D1MAD AMAPT-T005-D1MAD AMAPT-T006-D1MAD AMAPT-T007-D1MAD AMAPT-T009-D1MAD AMAPT-T011-D1MAD AMAPT-T012-D1MAD AMAPT-T013-D1MAD AMAPT-T014-D1MAD Diretiva Aves Diretiva Habitats Meta DQEM BEA