MS/Art8-2024/2024/D1-B/Netherlands/NE Atlantic: Greater North Sea

Member State report / Art8-2024 / 2024 / D1-B / Netherlands / NE Atlantic: Greater North Sea

Report type	Member State report to Commission
MSFD Article	Art8
Report due	2024-10-15
GES Descriptor	D1 Birds
Member State	Netherlands
Region/subregion	NE Atlantic: Greater North Sea
Report date	2026-04-10 12:40:24

Nederlands Continentaal Plat vanaf de basislijn (0 mijl) (ANS-NL-MS-1)

Simplified table

Regional assessment area	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea
Component MRUs
GES component	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B	D1B
Feature	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Pelagic-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Surface-feeding birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds	Wading birds
Element	Aythya marila	Aythya marila	Aythya marila	Aythya marila	Bucephala clangula	Bucephala clangula	Bucephala clangula	Bucephala clangula	Somateria mollissima	Somateria mollissima	Somateria mollissima	Somateria mollissima	Somateria mollissima	Somateria mollissima	Alca torda	Alca torda	Alca torda	Cepphus grylle	Cepphus grylle	Cepphus grylle	Fratercula arctica	Fratercula arctica	Fratercula arctica	Gulosus aristotelis	Gulosus aristotelis	Gulosus aristotelis	Gulosus aristotelis	Mergus serrator	Mergus serrator	Mergus serrator	Mergus serrator	Mergus serrator	Morus bassanus	Morus bassanus	Morus bassanus	Morus bassanus	Phalacrocorax carbo	Phalacrocorax carbo	Phalacrocorax carbo	Phalacrocorax carbo	Phalacrocorax carbo	Phalacrocorax carbo	Phalacrocorax carbo	Podiceps grisegena	Podiceps grisegena	Podiceps grisegena	Podiceps grisegena	Uria aalge	Uria aalge	Uria aalge	Uria aalge	Fulmarus glacialis	Fulmarus glacialis	Fulmarus glacialis	Larus argentatus	Larus argentatus	Larus argentatus	Larus argentatus	Larus argentatus	Larus argentatus	Larus canus	Larus canus	Larus canus	Larus canus	Larus canus	Larus canus	Larus fuscus	Larus fuscus	Larus fuscus	Larus fuscus	Larus fuscus	Larus fuscus	Larus fuscus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus ridibundus	Larus ridibundus	Larus ridibundus	Larus ridibundus	Larus ridibundus	Larus ridibundus	Rissa tridactyla	Rissa tridactyla	Rissa tridactyla	Stercorarius parasiticus	Stercorarius parasiticus	Stercorarius parasiticus	Stercorarius skua	Stercorarius skua	Stercorarius skua	Stercorarius skua	Sterna dougallii	Sterna dougallii	Sterna dougallii	Sterna hirundo	Sterna hirundo	Sterna hirundo	Sterna hirundo	Sterna hirundo	Sterna paradisaea	Sterna paradisaea	Sterna paradisaea	Sterna paradisaea	Sterna paradisaea	Sterna sandvicensis	Sterna sandvicensis	Sterna sandvicensis	Sterna sandvicensis	Sterna sandvicensis	Sternula albifrons	Sternula albifrons	Sternula albifrons	Sternula albifrons	Sternula albifrons	Sternula albifrons	Anas acuta	Anas acuta	Anas acuta	Anas acuta	Anas acuta	Anas crecca	Anas crecca	Anas crecca	Anas crecca	Anas crecca	Arenaria interpres	Arenaria interpres	Arenaria interpres	Arenaria interpres	Calidris alba	Calidris alba	Calidris alba	Calidris alba	Calidris alba	Calidris alpina	Calidris alpina	Calidris alpina	Calidris alpina	Calidris alpina	Calidris canutus	Calidris canutus	Calidris canutus	Calidris canutus	Calidris canutus	Calidris ferruginea	Calidris ferruginea	Calidris ferruginea	Calidris ferruginea	Calidris ferruginea	Calidris maritima	Calidris maritima	Calidris maritima	Calidris maritima	Calidris pugnax	Calidris pugnax	Calidris pugnax	Charadrius alexandrinus	Charadrius alexandrinus	Charadrius alexandrinus	Charadrius alexandrinus	Charadrius alexandrinus	Charadrius alexandrinus	Charadrius hiaticula	Charadrius hiaticula	Charadrius hiaticula	Charadrius hiaticula	Charadrius hiaticula	Charadrius hiaticula	Egretta garzetta	Egretta garzetta	Egretta garzetta	Egretta garzetta	Egretta garzetta	Egretta garzetta	Haematopus ostralegus	Haematopus ostralegus	Haematopus ostralegus	Haematopus ostralegus	Haematopus ostralegus	Haematopus ostralegus	Haematopus ostralegus	Limosa lapponica	Limosa lapponica	Limosa lapponica	Limosa lapponica	Limosa lapponica	Limosa limosa	Limosa limosa	Limosa limosa	Limosa limosa	Numenius arquata	Numenius arquata	Numenius arquata	Numenius arquata	Numenius arquata	Numenius phaeopus	Numenius phaeopus	Numenius phaeopus	Numenius phaeopus	Platalea leucorodia	Platalea leucorodia	Platalea leucorodia	Platalea leucorodia	Platalea leucorodia	Platalea leucorodia	Platalea leucorodia	Platalea leucorodia	Pluvialis squatarola	Pluvialis squatarola	Pluvialis squatarola	Pluvialis squatarola	Pluvialis squatarola	Recurvirostra avosetta	Recurvirostra avosetta	Recurvirostra avosetta	Recurvirostra avosetta	Recurvirostra avosetta	Recurvirostra avosetta	Tadorna tadorna	Tadorna tadorna	Tadorna tadorna	Tadorna tadorna	Tadorna tadorna	Tringa erythropus	Tringa erythropus	Tringa erythropus	Tringa erythropus	Tringa erythropus	Tringa nebularia	Tringa nebularia	Tringa nebularia	Tringa nebularia	Tringa totanus	Tringa totanus	Tringa totanus	Tringa totanus
Element extent
Trend element	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Deteriorating	Deteriorating	Deteriorating	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Deteriorating	Deteriorating	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Deteriorating	Deteriorating	Deteriorating	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Element 2	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	breeding	breeding	non-breeding	breeding	breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	breeding	breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	breeding	breeding	breeding	breeding	breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding
Element source	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR
Criterion	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2
Parameter			ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding		ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Breeding			ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	Fecundity rate		ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate		ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding		ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding	ABU-Breeding	Fecundity rate	Fecundity rate	ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding		ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Non-breeding			ABU-Non-breeding	ABU-Non-breeding	ABU-Breeding		ABU-Non-breeding	ABU-Non-breeding
Threshold value upper			0.7	28000.0			0.7	4600.0	0.7	6200.0		0.7	0.7	132000.0	0.7	0.991530327	65000.0	0.7			0.8	0.991547566	0.8	0.7	0.980383334	0.7	0.7			0.7	0.7	3000.0	0.8	0.993535472	0.7	17000.0	0.7	0.7	20000.0	0.984374887	0.7	0.7	28000.0			0.7	0.7	0.8	0.992647591	0.7	88000.0	0.8	0.994973039	0.8	0.7	0.7	0.988908295	1.0	0.7	0.7	0.7	0.7	0.986349452	1.0	0.7	0.7	0.7	0.7	92000.0	0.990674733	1.0	0.7	0.7	0.7	0.7	0.989389485	1.0	0.7	0.7	17000.0	0.7	0.7	0.98247489	1.0	0.7	0.7	0.7	0.987999825	0.7	0.7	0.988942563	0.7	0.7	0.992594823	0.7	190.0	0.7	0.989564047		0.7	29000.0	0.989758466	1.0	0.7	0.7	2250.0	0.989543847	1.0		0.7	28000.0	0.989944701	1.0	0.7	0.7	0.7	700.0	0.984654163	1.0	0.7			0.7	0.7	10000.0			0.7	0.7	40000.0			0.7	6100.0			0.7	0.7	4500.0			0.7	0.7	190000.0			0.7	0.7	51000.0			0.7	0.7	380.0			0.7	0.7			0.7	0.7	800.0	1.0	0.7	0.7	560.0	0.7	630.0	1.0	0.7	0.7	2400.0	0.7	65.0		0.7	0.7	400.0	0.7	0.7	0.992379984	1.0	0.7	0.7	260000.0			0.7	0.7	42000.0			0.7	0.7			0.7	0.7	86000.0			0.7	0.7	0.7	0.7	920.0	0.987053215	1.0	0.7	0.7	850.0			0.7	0.7	17000.0	0.7	6700.0	0.989339429	1.0	0.7	10200.0	0.7		0.7	0.7	41000.0			0.7	0.7	2400.0			0.7	0.7	0.7		0.7	23000.0
Threshold value lower
Threshold value operator			>=	>=			>=	>=	>=	>=		>=	>=	>=	>=	>=	>=	>=			>=	>=	>=	>=	>=	>=	>=			>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=			>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=		>=	>=	>=	>=	>=		>=	>=	>=	>=	>=	>=		>=	>=	>=	>=	>=		>=	>=	>=	>=	>=	>=		>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=	>=		>=	>=	>=		>=	>=	>=	>=			>=	>=	>=		>=	>=	>=	>=	>=		>=			>=	>=	>=			>=	>=	>=			>=	>=			>=	>=	>=			>=	>=	>=			>=	>=	>=			>=	>=	>=			>=	>=			>=	>=	>=		>=	>=	>=	>=	>=		>=	>=	>=	>=	>=		>=	>=	>=	>=	>=	>=		>=	>=	>=			>=	>=	>=			>=	>=			>=	>=	>=			>=	>=	>=	>=	>=	>=		>=	>=	>=			>=	>=	>=	>=	>=	>=		>=	>=	>=		>=	>=	>=			>=	>=	>=			>=	>=	>=		>=	>=
Threshold qualitative			0				0		0				0		0	0		0			0	0		0	0		0				0		0	0				0		0		0					0	0	0			0	0	0		0	0		0	0		0	0		0	0		0		0		0	0		0	0		0	0			0	0		0	0	0	0	0	0	0	0	0	0	0		0	0		0		0		0	0		0			0		0		0		0		0		0			0	0				0	0				0				0	0				0	0				0	0				0	0				0	0			0	0			0	0		0			0	0		0			0	0		0	0	0		0	0				0	0				0	0			0	0				0	0	0	0		0		0	0				0	0		0		0		0		0		0	0				0	0				0	0	0		0
Threshold value source			OSPAR Convention	BD			OSPAR Convention	BD	OSPAR Convention	BD		National	OSPAR Convention	BD	OSPAR Convention	OSPAR Convention	BD	OSPAR Convention			OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	National	OSPAR Convention			National	OSPAR Convention	BD	OSPAR Convention	OSPAR Convention	National	BD	National	OSPAR Convention	BD	OSPAR Convention	National	OSPAR Convention	BD			National	OSPAR Convention	OSPAR Convention	OSPAR Convention	National	BD	OSPAR Convention	OSPAR Convention	National	National	OSPAR Convention	OSPAR Convention	National	National	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	National	National	OSPAR Convention	National	OSPAR Convention	BD	OSPAR Convention	National	National	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	National	National	OSPAR Convention	BD	National	OSPAR Convention	OSPAR Convention	National	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	National	BD	OSPAR Convention	OSPAR Convention		OSPAR Convention	BD	OSPAR Convention	National	National	OSPAR Convention	BD	OSPAR Convention	National		OSPAR Convention	BD	OSPAR Convention	National	National	National	OSPAR Convention	BD	OSPAR Convention	National	National			National	OSPAR Convention	BD			National	OSPAR Convention	BD			OSPAR Convention	BD			National	OSPAR Convention	BD			National	OSPAR Convention	BD			National	OSPAR Convention	BD			National	OSPAR Convention	BD			National	OSPAR Convention			OSPAR Convention	OSPAR Convention	BD	National	National	OSPAR Convention	BD	OSPAR Convention	BD	National	National	OSPAR Convention	BD	National	BD		National	OSPAR Convention	BD	National	OSPAR Convention	OSPAR Convention	National	National	OSPAR Convention	BD			National	OSPAR Convention	BD			National	OSPAR Convention			National	OSPAR Convention	BD			National	OSPAR Convention	National	OSPAR Convention	BD	OSPAR Convention	National	National	OSPAR Convention	BD			National	OSPAR Convention	BD	OSPAR Convention	BD	OSPAR Convention	National	OSPAR Convention	BD	National		National	OSPAR Convention	BD			National	OSPAR Convention	BD			National	OSPAR Convention	National		OSPAR Convention	BD
Value achieved upper																1.013442067						0.984498959			1.000437216									1.041425651						1.012447697									0.995541202				0.980798112				0.946264439						0.924078377							0.980701301						0.957505109							0.906807351					0.963079003			0.921098194			0.970687304				1.055834215				0.952061014					0.948121257					1.005173917						1.005953347																																																																0.958536469																										1.023256641												0.961637814
Value achieved lower			0.109735789	21000.0			0.830697648	2700.0	0.421316598	4300.0		0.02	0.576949032	74000.0	1.406918569		94000.0	1.107679391			0.912440396		1.01	0.6189929		4.84	1.356877354			0.86	0.848677647	3000.0	2.763717915		1.41	20000.0	1.05	1.936108798	20000.0		16.6	1.817199791	43000.0			0.24	0.371370802	0.961056833		2.06	128000.0	0.608646243		0.24	0.7	0.605360261			0.37	0.677331621	0.27	0.347217835			0.49	0.870297026	3.65	1.287081209	46000.0			1.22	13.59062946	87.5	0.572585824			0.66	0.592547331	11000.0	0.46	0.555636182			1.8	0.993404217	0.362479318		1.98	0.149270535		0.62	0.890022854		1.54	240.0	2.371212268			0.518667253	15000.0			0.88	0.321529213	900.0				1.024483928	18000.0			3.39	3.3	0.737938156	860.0			1.09			1.65	1.626754168	13000.0			1.67	1.549570149	51000.0			0.801521211	4800.0			5.82	1.723961638	16500.0			1.36	0.64023871	270000.0			0.94	0.584670377	67000.0			1.17	0.573309511	430.0			0.89	0.662966006			0.479897349	0.469626604	150.0		0.27	0.450778723	50.0	1.041194235	350.0		1.57	1.002441677	4600.0	65.3	65.0		189.9	47.14715807	400.0	0.35	0.492521702			0.53	0.580358974	130000.0			1.57	0.885822916	66000.0				2.384321292			1.11	1.010797754	126000.0				1.072367423	6.18	4.417318583	3275.0			5.46	12.88670597	2800.0			1.16	0.698259438	32000.0	0.531623079	5500.0			1.000157119	8200.0	1.22		1.65	1.092317284	65000.0			0.48	0.566133939	1000.0			0.72	0.889664141			0.7529306	20000.0
Value unit			Other	Other			Other	Other	Other	Other		Other	Other	Other	Other	Other	Other	Other			Other	Other	Other	Other	Other	Other	Other			Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other			Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other		Other	Other	Other	Other	Other	Other	Other	Other	Other		Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other			Other	Other	Other			Other	Other	Other			Other	Other			Other	Other	Other			Other	Other	Other			Other	Other	Other			Other	Other	Other			Other	Other			Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other		Other	Other	Other	Other	Other	Other	Other	Other	Other	Other			Other	Other	Other			Other	Other			Other	Other	Other			Other	Other	Other	Other	Other	Other	Other	Other	Other	Other			Other	Other	Other	Other	Other	Other	Other	Other	Other	Other		Other	Other	Other			Other	Other	Other			Other	Other	Other		Other	Other
Proportion threshold value			100.0	100.0			100.0	100.0	100.0	100.0		100.0	100.0	100.0	100.0	100.0	100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0		100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0		100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0			100.0	100.0	100.0			100.0	100.0	100.0			100.0	100.0			100.0	100.0	100.0			100.0	100.0	100.0			100.0	100.0	100.0			100.0	100.0	100.0			100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0		100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0			100.0	100.0	100.0			100.0	100.0			100.0	100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0		100.0	100.0	100.0			100.0	100.0	100.0			100.0	100.0	100.0		100.0	100.0
Proportion value achieved							100.0								100.0	100.0	100.0	100.0			100.0		100.0		100.0	100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0					100.0	100.0	100.0	100.0															100.0	100.0	100.0	100.0			100.0	100.0	100.0											100.0	100.0			100.0				100.0		100.0	100.0	100.0	100.0						100.0						100.0		100.0		100.0	100.0	100.0	100.0	100.0		100.0			100.0	100.0	100.0			100.0	100.0	100.0			100.0					100.0	100.0			100.0		100.0					100.0			100.0		100.0			100.0											100.0			100.0	100.0	100.0	100.0	100.0		100.0	100.0	100.0										100.0	100.0	100.0				100.0			100.0	100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0		100.0	100.0	100.0			100.0		100.0					100.0				100.0	100.0	100.0								100.0	100.0	0.8		100.0
Proportion threshold value unit			% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value		% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value		% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value		% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value		% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value		% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value			% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value		% of population achieving threshold value	% of population achieving threshold value
Trend parameter			Unknown	Unknown			Unknown	Unknown	Deteriorating	Unknown		Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown			Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown			Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown			Unknown	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown		Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown		Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Unknown			Unknown	Unknown	Unknown			Unknown	Unknown	Unknown			Unknown	Unknown			Unknown	Unknown	Unknown			Unknown	Unknown	Unknown			Unknown	Unknown	Unknown			Unknown	Unknown	Unknown			Unknown	Deteriorating			Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown		Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown			Unknown	Unknown	Unknown			Unknown	Unknown			Unknown	Unknown	Unknown			Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown			Unknown	Deteriorating	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown		Unknown	Unknown	Unknown			Unknown	Unknown	Unknown			Unknown	Unknown	Unknown		Unknown	Unknown
Parameter achieved			No	No			Yes	No	No	No		No	No	No	Yes	Yes	Yes	Yes			Yes	No	Yes	No	Yes	Yes	Yes			Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes			No	No	Yes	Yes	Yes	Yes	No	No	No	No	No	No	No	No	No	No	No	No	No	No	Yes	Yes	Yes	Yes	No	No	Yes	Yes	Yes	No	No	Yes	No	No	No	No	No	No	No	Yes	Yes	No	No	Yes	No	No	No	Yes	No	Yes	Yes	Yes	Yes		No	No	No	Unknown	Yes	No	No	No	No		Yes	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Unknown	Yes			Yes	Yes	Yes			Yes	Yes	Yes			Yes	No			Yes	Yes	Yes			Yes	No	Yes			Yes	No	Yes			Yes	No	Yes			Yes	No			No	No	No	No	No	No	No	Yes	No	No	Yes	Yes	Yes	Yes	Yes		Yes	Yes	Yes	No	No	No	No	No	No	No			Yes	Yes	Yes			Yes	Yes			Yes	Yes	Yes			Yes	Yes	Yes	Yes	Yes	Yes	Unknown	Yes	Yes	Yes			Yes	No	Yes	No	No	No	No	Yes	No	Yes		Yes	Yes	Yes			No	No	No			Yes	Yes	Yes		Yes	No
Description parameter			The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.		Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.			The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.		The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.		The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.			The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.		Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The breeding success of seabirds can reflect changes in habitat long before these become visible as changes in population size. The results of this assessment can therefore provide an early warning of changes in population status. They complement the assessment of population size (D1C2). Only the assessments agreed in OSPAR were used for the final assessment.	In addition to the OSPAR assessment, specific national information is included on breeding success. The national data broadly reflect the same picture as the regional indicators. Differences are mainly attributable to geographical coverage and the fact that some of the species involved are different.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.		Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.			Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.	The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis The OSPAR indicator B1 for abundance of seabirds in the International North Sea is based on the numbers of breeding pairs counted in breeding colonies, the vast majority of which are located outside the Netherlands, for most species of 'true seabirds'. The indicator therefore reflects how well or poorly seabird populations are doing in the North Sea in general, but less so the specific circumstances in the Dutch part of it. In addition, seabirds present in our part of the North Sea are monitored in the Netherlands by means of aircraft counts. This data is so far not used in the formal OSPAR assessment. These data, together with data from the Belgian and German parts of the North Sea, have been processed in a pilot indicator Marine Bird Abundance ? non-breeding offshore birds, but because this has not yet been sufficiently developed, the Netherlands has carried out an analysis to supplement the OSPAR analysis. about our part of the North Sea. Trends are calculated in the Ecological Monitoring Network (NEM) based on Dutch aircraft counts and data from sea migration counts from the coast (see Sovon website). For the additional analysis, the NEM trend data for most species were processed in the same way as for the OSPAR indicator (baseline 1991-2000, assessment value average over 2014-2020, threshold value 70%/80% of baseline). Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.		The population abundance is the most important criterion against which the general status of birds is assessed. The OSPAR analysis for the International North Sea was used for the assessment.	Explanation of additional national analysis. For several bird species, """"""""""""""""favorable reference values"""""""""""""""" have been established for the """"""""""""""""population"""""""""""""""" aspect of their conservation status. For these species, it was determined whether the (seasonal average) numbers in the Netherlands are equal to or greater than the favorable reference values. Only the assessments agreed in OSPAR were used for the final assessment. This Dutch assessment therefore does not count in the final GES assessment.
Related indicator			marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023		NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-abundance-qsr23-ospar			marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_2023	NL-D1B-D1C2_NL_Birds Directive_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_2023	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C2_NL_2023	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar		marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023		marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar			marine-bird-abundance-qsr23-ospar	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	NL-D1B-D1C2_NL_2023	NL-D1B-D1C2_NL_Birds Directive_2023		NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	marine-bird-breeding-productivity-qsr23-ospar	NL-D1B-D1C3_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023	NL-D1B-D1C2_NL_2023		NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023			NL-D1B-D1C2_NL_2023	marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_2023		marine-bird-abundance-qsr23-ospar	NL-D1B-D1C2_NL_Birds Directive_2023
Criteria status	Unknown	Unknown	Not good	Not good	Unknown	Unknown	Good	Good	Not good	Not good	Unknown	Not good	Not good	Not good	Good	Good	Unknown	Good	Unknown	Unknown	Good	Not good	Unknown	Not good	Good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Good	Good	Good	Unknown	Unknown	Not good	Not good	Good	Good	Unknown	Unknown	Not good	Not good	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Not good	Not good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Not good	Not good	Unknown	Not good	Not good	Unknown	Good	Not good	Unknown	Unknown	Good	Good	Unknown	Not good	Not good	Not good	Not good	Unknown	Not good	Not good	Not good	Not good	Unknown	Good	Good	Good	Good	Unknown	Good	Good	Good	Good	Good	Unknown	Unknown	Unknown	Good	Good	Good	Unknown	Unknown	Good	Good	Good	Unknown	Unknown	Good	Good	Unknown	Unknown	Good	Good	Good	Unknown	Unknown	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Unknown	Unknown	Not good	Not good	Not good	Unknown	Not good	Not good	Not good	Good	Good	Unknown	Good	Good	Good	Unknown	Unknown	Unknown	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Unknown	Unknown	Good	Good	Good	Unknown	Unknown	Good	Good	Unknown	Unknown	Good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Unknown	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Unknown	Unknown	Good	Good	Good	Unknown	Unknown	Not good	Not good	Not good	Unknown	Unknown	Good	Good	Unknown	Unknown	Good	Good
Description criteria	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	In the International North Sea, the breeding success of seabirds is so low for the majority of the assessed species that, if this does not improve, these species will probably eventually receive Red List status, if they do not already have it. Bird species that forage at sea for fish in the upper water layers in particular do poorly in this respect. This includes most seabirds breeding in the Netherlands. Only 39 percent of the assessed species have a breeding success that meets the threshold value. Among surface foragers this is 21 percent and among birds of the intertidal area 33 percent. The breeding success of birds that forage deeper in the water column is good for most species (83 percent). The status at criterion level is unchanged compared to the previous assessment period.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.	The population abundance of seabirds (numbers of individuals outside the breeding season or pairs in breeding colonies) is used as an indicator because this quantity is practically measurable and suitable for assessing long-term changes in the bird community. Changes in the population can indicate human-induced effects and can be a reason for taking management measures. The OSPAR indicator B1 Marine bird abundance is used to assess the population abundance of birds in the International North Sea.
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Description element	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.	The assessment of the current status of seabirds is based on data on population abundance (criterion D1C2, OSPAR assessment) and breeding productivity (D1C3, OSPAR assessment). There is still too little knowledge on the relative influence of different pressures and on cumulative effects for birds. This is why criteria D1C1 Incidental by-catch and D1C5 Quality of habitat are not yet part of the overall assessment.
Source assessment feature	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR
Reporting method feature	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A
Trend feature	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other
Integration rule description criteria	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.	OSPAR Thematic assessment. The integrated assessment per element is based on information on the population abundance (D1C2) and breeding success (D1C3) of seabirds in the International North Sea.
GES extent threshold	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00
GES extent achieved	25.00	25.00	25.00	25.00	25.00	25.00	25.00	25.00	25.00	25.00	25.00	25.00	25.00	25.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	82.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	42.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00	58.00
GES extent unit	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group	Proportion of species in good status within species group
GES achieved	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported
Description overall status	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.	To assess the current situation, the Netherlands uses the regional assessment of the international North Sea (OSPAR region II, Greater North Sea; OSPAR, 2023). In addition, the Netherlands reports specifically on seabirds in the Dutch part of the North Sea, largely based on aircraft census data that did not fit into the OSPAR analysis. This information is not part of the integrated assessment, but does provide an additional picture of the situation in the Dutch part of the North Sea. For the same purpose, additional information has been included about birds breeding in the Netherlands.
Assessments period	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017
Related pressures	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)	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)
Related targets	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7	ANSNL-D1B-T1.5 ANSNL-D1B-T1.6 ANSNL-D1B-T1.7a ANSNL-D1B-T1.7b ANSNL-D1B-T1.8 ANSNL-D1B-T1.9 ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1T1 ANSNL-D1T7
Test TV	NA	NA	No	NA	NA	NA	No	NA	No	NA	NA	NA	No	NA	No	Yes	NA	No	NA	NA	No	No	NA	No	Yes	NA	No	NA	NA	NA	No	NA	No	Yes	NA	NA	NA	No	NA	Yes	NA	No	NA	NA	NA	NA	No	No	Yes	NA	NA	No	No	No	NA	No	No	NA	No	No	NA	No	No	NA	No	No	NA	No	NA	No	NA	No	No	NA	No	No	NA	No	No	NA	NA	No	No	NA	No	No	No	No	No	No	No	No	No	No	No	NA	No	Yes	NA	No	NA	No	NA	No	No	NA	No	NA	NA	No	NA	Yes	NA	No	NA	No	NA	Yes	NA	No	NA	NA	No	No	NA	NA	NA	No	No	NA	NA	NA	No	NA	NA	NA	No	No	NA	NA	NA	No	No	NA	NA	NA	No	No	NA	NA	NA	No	No	NA	NA	NA	No	No	NA	NA	No	No	NA	NA	No	No	NA	No	NA	NA	No	No	NA	No	NA	NA	No	No	NA	No	No	No	NA	No	No	NA	NA	NA	No	No	NA	NA	NA	No	No	NA	NA	No	No	NA	NA	NA	No	No	No	No	NA	Yes	NA	No	No	NA	NA	NA	No	No	NA	No	NA	No	NA	No	NA	No	NA	No	No	NA	NA	NA	No	No	NA	NA	NA	No	No	NA	NA	No	NA
Test results	False	False	Correct	False	False	False	False	False	Correct	False	False	False	Correct	False	False	Correct	False	False	False	False	False	Correct	False	Correct	Correct	False	False	False	False	False	False	False	False	Correct	False	False	False	False	False	Correct	False	False	False	False	False	False	Correct	False	Correct	False	False	Correct	Correct	Correct	False	Correct	Correct	False	Correct	Correct	False	Correct	Correct	False	Correct	False	False	False	False	Correct	False	False	False	False	Correct	Correct	False	Correct	Correct	False	False	Correct	Correct	False	False	False	Correct	Correct	False	Correct	Correct	Correct	False	Correct	False	False	False	Correct	False	Correct	False	Correct	Correct	False	Correct	False	Correct	False	False	False	False	Correct	False	False	False	False	False	Correct	Correct	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	Correct	False	False	False	False	Correct	False	False	False	False	Correct	False	False	False	False	Correct	False	False	Correct	Correct	False	False	Correct	Correct	False	False	False	False	False	False	False	False	False	False	False	False	False	Correct	Correct	Correct	False	Correct	Correct	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	Correct	Correct	False	False	False	False	False	False	Correct	False	Correct	False	Correct	False	False	False	False	False	False	False	False	False	False	Correct	Correct	False	False	False	False	False	False	False	False	False