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

Member State report / Art8-2024 / 2024 / D1-B / Belgium / 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	Belgium
Region/subregion	NE Atlantic: Greater North Sea
Report date	2026-01-13 14:08:15

Belgian Part of the North Sea (ANS-BE-MS-1)

Simplified table

Regional assessment area	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-ospar-Greater North Sea	marine-bird-abundance-qsr23-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
Feature	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Benthic-feeding birds	Grazing birds	Grazing birds	Grazing birds	Grazing birds	Grazing birds	Grazing 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	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	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
Element	Aythya marila	Bucephala clangula	Clangula hyemalis	Melanitta nigra	Somateria mollissima	Somateria mollissima	Somateria spectabilis	Anas platyrhynchos	Branta bernicla	Branta leucopsis	Branta leucopsis	Mareca penelope	Spatula clypeata	Alca torda	Alca torda	Alca torda	Alca torda	Alca torda	Alca torda	Alca torda	Cepphus grylle	Cepphus grylle	Cepphus grylle	Fratercula arctica	Fratercula arctica	Gavia spp.	Gulosus aristotelis	Gulosus aristotelis	Gulosus aristotelis	Mergus serrator	Morus bassanus	Morus bassanus	Morus bassanus	Morus bassanus	Morus bassanus	Morus bassanus	Morus bassanus	Phalacrocorax carbo	Phalacrocorax carbo	Phalacrocorax carbo	Podiceps cristatus	Podiceps cristatus	Podiceps cristatus	Podiceps grisegena	Uria aalge	Uria aalge	Uria aalge	Uria aalge	Uria aalge	Uria aalge	Uria aalge	Uria lomvia	Chroicocephalus ridibundus	Chroicocephalus ridibundus	Chroicocephalus ridibundus	Fulmarus glacialis	Fulmarus glacialis	Hydrobates pelagicus	Hydrocoloeus minutus	Ichthyaetus melanocephalus	Larus argentatus	Larus argentatus	Larus argentatus	Larus argentatus	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 canus	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 fuscus	Larus fuscus	Larus fuscus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Larus marinus	Puffinus puffinus	Rissa tridactyla	Rissa tridactyla	Rissa tridactyla	Rissa tridactyla	Rissa tridactyla	Rissa tridactyla	Rissa tridactyla	Stercorarius parasiticus	Stercorarius parasiticus	Stercorarius skua	Stercorarius skua	Sterna dougallii	Sterna dougallii	Sterna hirundo	Sterna hirundo	Sterna paradisaea	Sterna paradisaea	Sternula albifrons	Sternula albifrons	Thalasseus sandvicensis	Thalasseus sandvicensis	Anas acuta	Anas crecca	Arenaria interpres	Calidris alba	Calidris alpina	Calidris canutus	Calidris ferruginea	Calidris maritima	Calidris pugnax	Charadrius alexandrinus	Charadrius alexandrinus	Charadrius hiaticula	Charadrius hiaticula	Egretta garzetta	Haematopus ostralegus	Haematopus ostralegus	Haematopus ostralegus	Limosa lapponica	Limosa limosa	Numenius arquata	Numenius phaeopus	Platalea leucorodia	Platalea leucorodia	Platalea leucorodia	Pluvialis apricaria	Pluvialis squatarola	Recurvirostra avosetta	Recurvirostra avosetta	Recurvirostra avosetta	Tadorna tadorna	Tringa erythropus	Tringa nebularia	Tringa totanus
Element extent
Trend element	Unknown	Unknown	Unknown	Unknown	Deteriorating	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	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	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	Deteriorating	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
Element 2	non-breeding	non-breeding	non-breeding		breeding	non-breeding	non-breeding	non-breeding	non-breeding	breeding	non-breeding	non-breeding	non-breeding						breeding	breeding	breeding	breeding	non-breeding	breeding	breeding		breeding	breeding	non-breeding	non-breeding						breeding	breeding	breeding	breeding	non-breeding			non-breeding	non-breeding						breeding	breeding	breeding	breeding	breeding	non-breeding	breeding	breeding	breeding		breeding								breeding	breeding	non-breeding											breeding	breeding	non-breeding								breeding	breeding	non-breeding								breeding	breeding	non-breeding	breeding						breeding	breeding	breeding	breeding	breeding	breeding	breeding	breeding	breeding	breeding	breeding	breeding	breeding	breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	non-breeding	non-breeding	non-breeding	non-breeding	non-breeding	non-breeding	breeding	non-breeding	breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	breeding	breeding	non-breeding	non-breeding	non-breeding	non-breeding	non-breeding
Element source	OSPAR	OSPAR	OSPAR	National	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	National	National	National	National	National	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	National	OSPAR	OSPAR	OSPAR	OSPAR	National	National	National	National	National	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	National	National	OSPAR	OSPAR	National	National	National	National	National	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	National	OSPAR	National	National	National	National	National	National	National	OSPAR	OSPAR	OSPAR	National	National	National	National	National	National	National	National	National	National	OSPAR	OSPAR	OSPAR	National	National	National	National	National	National	National	OSPAR	OSPAR	OSPAR	National	National	National	National	National	National	National	OSPAR	OSPAR	OSPAR	OSPAR	National	National	National	National	National	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	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	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C3	D1C2	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C3	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C3	D1C2	D1C3	D1C2	D1C3	D1C2	D1C3	D1C2	D1C3	D1C2	D1C3	D1C2	D1C3	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C3	D1C2	D1C2	D1C2	D1C2	D1C2
Parameter	Abundance	Abundance		Abundance	Abundance	Abundance		Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance			Abundance	Fecundity rate	Abundance	Abundance	Fecundity rate	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Abundance	Abundance		Abundance	Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance	Fecundity rate		Abundance	Fecundity rate	Abundance	Abundance	Fecundity rate		Abundance		Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance		Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Fecundity rate	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance	Abundance	Abundance	Abundance	Abundance	Abundance	Fecundity rate	Abundance		Abundance	Abundance	Fecundity rate	Abundance	Abundance	Abundance	Abundance	Abundance
Threshold value upper	0.7	0.7		0.5	0.7	0.7		0.7	0.7	0.7	0.7	0.7	0.7	0.5	0.8	0.5	0.8	0.991530327	0.8	0.991530327	0.7			0.8	0.991547566	0.5	0.7	0.980383334	0.7	0.7	0.5	0.8	0.5	0.8	0.99353547207	0.8	0.99353547207	0.7	0.9843748869	0.7	0.5	0.5		0.7	0.5	0.8	0.5	0.8	0.992647591	0.8	0.992647591		0.7	0.98247489015	0.7	0.8	0.99497303932		0.5		0.5	0.7	0.7	0.5	0.7	0.7	0.988908295	0.7	0.988908295	0.7	0.5	0.7	0.7	0.5	0.7	0.7	0.5	0.7	0.7	0.986349452	0.7	0.986349452	0.7	0.5	0.7	0.7	0.5	0.7	0.7	0.99067473341	0.7	0.99067473341	0.7	0.5	0.7	0.7	0.5	0.7	0.7	0.98938948462	0.7	0.98938948462	0.7		0.5	0.7	0.5	0.7	0.9879998247	0.7	0.9879998247	0.7	0.98894256284	0.7	0.9925948233	0.7	0.989564047	0.7	0.98975846594	0.7	0.98954384743	0.7	0.9846541632	0.7	0.98994470073	0.7	0.7	0.7	0.7	0.7	0.7	0.7	0.7	0.7	0.7	0.7	0.7	0.7	0.7	0.7	0.99237998392	0.7	0.7	0.7	0.7	0.7	0.7	0.9870532147	0.7		0.7	0.7	0.98933942854	0.7	0.7	0.7	0.7	0.7
Threshold value lower
Threshold value operator
Threshold qualitative
Threshold value source	OSPAR Convention	OSPAR Convention		National	OSPAR Convention	OSPAR Convention		OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention			OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	National	National		OSPAR Convention	National	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention		OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention		National		National	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention		National	OSPAR Convention	National	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention		OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention
Value achieved upper																		1.013442067		1.013442067					0.984498959			1.0004372159							1.0414256509		1.0414256509		1.0124476973										0.995541202		0.995541202			0.90680735072			0.98079811193										0.94626443901		0.94626443901											0.92407837682		0.92407837682								0.980701301		0.980701301								0.957505109		0.957505109							0.96307900318		0.96307900318		0.92109819376		0.97068730372		1.0558342154		0.95206101354		0.94812125704		1.0059533474		1.0051739173																0.95853646938							1.0232566406					0.961637814
Value achieved lower	0.10973578914	0.83069764786			0.42131659799	0.57694903186		0.91692716915	0.79330924097	12.008761407	1.6861023715	0.82375286921	2.0195681744		1.4069185694		1.4069185694		1.4069185694		1.1076793915			0.91244039599			0.61899290008		1.356877354	0.84867764724		2.763717915		2.763717915		2.763717915		1.9361087982		1.8171997912				0.37137080189		0.96105683298		0.96105683298		0.96105683298			0.55563618249		0.99340421666	0.60864624337						0.60536026112	0.67733162147		0.60536026112	0.67733162147		0.60536026112		0.67733162147		0.34721783546	0.87029702598		0.34721783546	0.87029702598		0.34721783546	0.87029702598		0.34721783546		0.87029702598		1.2870812088	13.590629459		1.2870812088	13.590629459		1.2870812088		13.590629459		0.5725858243	0.59254733081		0.5725858243	0.59254733081		0.5725858243		0.59254733081			0.36247931763		0.36247931763		0.36247931763		0.14927053542		0.89002285391		2.3712122681		0.51866725259		0.32152921285		0.73793815565		1.0244839283		1.6267541683	1.5495701489	0.80152121104	1.7239616384	0.64023870991	0.58467037657	0.57330951132	0.66296600577	0.47989734911	0.46962660443	0.45077872269	1.0411942348	1.0024416774	47.147158071	0.49252170161		0.58035897398	0.88582291632	2.3843212922	1.0107977536	1.0723674235	4.4173185831		12.886705971		0.69825943824	0.53162307906		1.0001571186	1.0923172843	0.56613393897	0.88966414078	0.75293060047
Value unit	index - relative abundance	index - relative abundance			index - relative abundance	index - relative abundance		index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance		index - relative abundance		index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance			index - relative abundance	Rate - population growth expected		index - relative abundance	Rate - population growth expected	index - relative abundance	index - relative abundance		index - relative abundance		index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance				index - relative abundance		index - relative abundance		index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected		index - relative abundance	Rate - population growth expected	index - relative abundance	index - relative abundance	Rate - population growth expected					index - relative abundance	index - relative abundance		index - relative abundance	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance		index - relative abundance	index - relative abundance		index - relative abundance	index - relative abundance		index - relative abundance	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance		index - relative abundance	index - relative abundance		index - relative abundance	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance		index - relative abundance	index - relative abundance		index - relative abundance	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance			index - relative abundance		index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance	Rate - population growth expected	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	Rate - population growth expected	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	Rate - population growth expected	index - relative abundance		index - relative abundance	index - relative abundance	Rate - population growth expected	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance	index - relative abundance
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter	Unknown	Unknown		Unknown	Deteriorating	Unknown		Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Improving	Unknown	Improving	Unknown	Unknown			Unknown	Improving	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown		Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Improving		Unknown	Stable	Unknown	Unknown	Deteriorating		Unknown		Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Deteriorating	Unknown	Deteriorating	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Stable	Unknown	Unknown	Deteriorating	Unknown	Unknown	Deteriorating	Unknown	Stable	Deteriorating	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Stable	Unknown		Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Stable	Unknown	Stable	Unknown	Deteriorating	Unknown	Stable	Unknown	Deteriorating	Unknown	Deteriorating	Unknown	Stable	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Deteriorating	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown		Deteriorating	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	No	Yes		No	No	No		Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes			Yes	No	No	No	Yes	Yes	Yes	Unknown	Yes	Unknown	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes		No	No	Yes	No	Yes	Yes	Yes	Yes		No	No	Yes	No	No		No		No	No	No	No	No	No	No	No	No	No	No	No	Yes	No	No	Yes	No	No	Yes	No	No	No	Yes	No	Yes	Yes	No	Yes	Yes	No	Yes	No	Yes	No	No	No	No	No	No	No	No	No	No		No	No	No	No	No	No	No	No	No	Yes	No	Yes	Yes	No	No	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	No	No	No	No	No	No	Yes	Yes	Yes	No	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes		No	No	No	Yes	Yes	No	Yes	Yes
Description parameter				Counts of seabirds at sea (SAS)										Counts of seabirds at sea (SAS)		Counts of seabirds at sea (SAS)		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods					Trend compares IA2017 and QSR2023 assessments, which used different methods	Counts of seabirds at sea (SAS)		Trend compares IA2017 and QSR2023 assessments, which used different methods			Counts of seabirds at sea (SAS)		Counts of seabirds at sea (SAS)		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Counts of seabirds at sea (SAS)	Counts of seabirds at sea (SAS)			Counts of seabirds at sea (SAS)		Counts of seabirds at sea (SAS)		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods			Trend compares IA2017 and QSR2023 assessments, which used different methods			Trend compares IA2017 and QSR2023 assessments, which used different methods		Counts of seabirds at sea (SAS)		Counts of seabirds at sea (SAS)			Counts of seabirds at sea (SAS)			Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Counts of seabirds at sea (SAS)			Counts of seabirds at sea (SAS)			Counts of seabirds at sea (SAS)			Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Counts of seabirds at sea (SAS)			Counts of seabirds at sea (SAS)			Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Counts of seabirds at sea (SAS)			Counts of seabirds at sea (SAS)			Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods			Counts of seabirds at sea (SAS)		Counts of seabirds at sea (SAS)		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods		Trend compares IA2017 and QSR2023 assessments, which used different methods																Trend compares IA2017 and QSR2023 assessments, which used different methods							Trend compares IA2017 and QSR2023 assessments, which used different methods					Trend compares IA2017 and QSR2023 assessments, which used different methods
Related indicator	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar		ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar		ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar			ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-SEA-2024		ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar		ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar		ANS-BE-BIRD-ABU-SEA-2024		ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar		ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-SEA-2024	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar		ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-PROD-2024; marine-bird-breeding-productivity-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar	ANS-BE-BIRD-ABU-2024; marine-bird-abundance-qsr23-ospar
Criteria status	Not good	Good	Unknown	Not good	Not good	Not good	Unknown	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Unknown	Unknown	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Good	Good	Good	Unknown	Unknown	Not good	Good	Good	Not good	Not good	Good	Good	Good	Unknown	Not good	Not good	Good	Not good	Not good	Unknown	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	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Not good	Not good	Not good	Not good	Good	Not good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Not good	Good	Good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Unknown	Not good	Not good	Not good	Good	Good	Not good	Good	Good
Description criteria				At sea (BE)												At sea (BE)	At sea (BE)									At sea (BE)							At sea (BE)	At sea (BE)							At sea (BE)						At sea (BE)	At sea (BE)											At sea (BE)					At sea (BE)	At sea (BE)	At sea (BE)											At sea (BE)	At sea (BE)	At sea (BE)								At sea (BE)	At sea (BE)	At sea (BE)								At sea (BE)	At sea (BE)	At sea (BE)								At sea (BE)	At sea (BE)
Element status	Not good	Good	Unknown	Not good	Not good	Not good	Unknown	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Unknown	Good	Good	Not good	Not good	Not good	Good	Good	Unknown	Unknown	Unknown	Unknown	Unknown	Good	Good	Good	Good	Good	Good	Good	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Unknown	Not good	Not good	Good	Not good	Not good	Unknown	Not good	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	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	Not good	Good	Good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Unknown	Not good	Not good	Not good	Good	Good	Not good	Good	Good
Description element	Topper	Brilduiker	IJseend	At sea: Zwarte zee-eend	Common Eider - Eider	Common Eider - Eider	Koningseider	Mallard - Wilde eend	Rotgans	Brandgans	Brandgans	Smient	Slobeend	At sea: Razorbill - Alk	At sea: Razorbill - Alk	At sea: Razorbill - Alk	At sea: Razorbill - Alk	At sea: Razorbill - Alk	Razorbill - Alk	Razorbill - Alk	Black guillemot - Zwarte zeekoet	Black guillemot - Zwarte zeekoet	Black guillemot - Zwarte zeekoet	Puffin - Papegaaiduiker	Puffin - Papegaaiduiker	At sea: Duiker spp.	Kuifaalscholver	Kuifaalscholver	Kuifaalscholver	Red-breasted merganser - Middelste zaagbek	At sea: Northern gannet - Jan van gent	At sea: Northern gannet - Jan van gent	At sea: Northern gannet - Jan van gent	At sea: Northern gannet - Jan van gent	At sea: Northern gannet - Jan van gent	Northern gannet - Jan van gent	Northern gannet - Jan van gent	Great cormorant - Aalscholver	Great cormorant - Aalscholver	Great cormorant - Aalscholver	At sea: Fuut - Geoorde fuut	At sea: Fuut - Geoorde fuut	Fuut - Geoorde fuut	Roodhalsfuut	At sea: Common guillemot - Zeekoet	At sea: Common guillemot - Zeekoet	At sea: Common guillemot - Zeekoet	At sea: Common guillemot - Zeekoet	At sea: Common guillemot - Zeekoet	Common guillemot - Zeekoet	Common guillemot - Zeekoet	Kortbekzeekoet	Kokmeeuw	Kokmeeuw	Kokmeeuw	Northern Fulmar - Noordse stormvogel	Northern Fulmar - Noordse stormvogel	Stormvogeltje	At sea: Dwergmeeuw	Zwartkopmeeuw	At sea: Herring gull - Europese Zilvermeeuw	At sea: Herring gull - Europese Zilvermeeuw	At sea: Herring gull - Europese Zilvermeeuw	At sea: Herring gull - Europese Zilvermeeuw	At sea: Herring gull - Europese Zilvermeeuw	At sea: Herring gull - Europese Zilvermeeuw	At sea: Herring gull - Europese Zilvermeeuw	Herring gull - Zilvermeeuw	Herring gull - Zilvermeeuw	Herring gull - Zilvermeeuw	At sea: Common gull - Stormmeeuw	At sea: Common gull - Stormmeeuw	At sea: Common gull - Stormmeeuw	At sea: Common gull - Stormmeeuw	At sea: Common gull - Stormmeeuw	At sea: Common gull - Stormmeeuw	At sea: Common gull - Stormmeeuw	At sea: Common gull - Stormmeeuw	At sea: Common gull - Stormmeeuw	At sea: Common gull - Stormmeeuw	Common gull - Stormmeeuw	Common gull - Stormmeeuw	Common gull - Stormmeeuw	At sea: Lesser black-backed gull - Kleine mantelmeeuw -	At sea: Lesser black-backed gull - Kleine mantelmeeuw -	At sea: Lesser black-backed gull - Kleine mantelmeeuw -	At sea: Lesser black-backed gull - Kleine mantelmeeuw -	At sea: Lesser black-backed gull - Kleine mantelmeeuw -	At sea: Lesser black-backed gull - Kleine mantelmeeuw -	At sea: Lesser black-backed gull - Kleine mantelmeeuw -	Lesser black-backed gull - Kleine mantelmeeuw -	Lesser black-backed gull - Kleine mantelmeeuw -	Lesser black-backed gull - Kleine mantelmeeuw -	At sea: Great black-backed gull - Grote mantelmeeuw	At sea: Great black-backed gull - Grote mantelmeeuw	At sea: Great black-backed gull - Grote mantelmeeuw	At sea: Great black-backed gull - Grote mantelmeeuw	At sea: Great black-backed gull - Grote mantelmeeuw	At sea: Great black-backed gull - Grote mantelmeeuw	At sea: Great black-backed gull - Grote mantelmeeuw	Great black-backed gull - Grote mantelmeeuw	Great black-backed gull - Grote mantelmeeuw	Great black-backed gull - Grote mantelmeeuw	Noordse pijlstormvogel	At sea: Black-legged kittiwake - Drieteenmeeuw	At sea: Black-legged kittiwake - Drieteenmeeuw	At sea: Black-legged kittiwake - Drieteenmeeuw	At sea: Black-legged kittiwake - Drieteenmeeuw	At sea: Black-legged kittiwake - Drieteenmeeuw	Black-legged kittiwake - Drieteenmeeuw	Black-legged kittiwake - Drieteenmeeuw	Arctic skua - Kleine jager	Arctic skua - Kleine jager	Great skua - Grote jager	Great skua - Grote jager	Roseate tern - Dougalls stern	Roseate tern - Dougalls stern	common tern - Visdief	common tern - Visdief	Arctic tern - Noordse Stern	Arctic tern - Noordse Stern	Dwergstern - little tern	Dwergstern - little tern	Grote stern	Grote stern	Pijlstaart	Wintertaling	Steenloper	Drieteenstrandloper	Bonte strandloper	Kanoet	Krombekstrandloper	Paarse strandloper	Kemphaan	Kentish plover - Strandplevier	Kentish plover - Strandplevier	Ringed plover - Bontbekplevier	Ringed plover - Bontbekplevier	Kleine zilverreiger	Oystercatcher - Scholekster	Oystercatcher - Scholekster	Oystercatcher - Scholekster	Rosse grutto	Grutto	Wulp	Regenwulp	Eurasian spoonbill - Lepelaar	Eurasian spoonbill - Lepelaar	Eurasian spoonbill - Lepelaar	Goudplevier	Zilverplevier	Pied avocet - Kluut	Pied avocet - Kluut	Pied avocet - Kluut	Shelduck - Bergeend	Zwarte ruiter	Groenpootruiter	Tureluur
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
Reporting method feature	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type A	Type A	Type A	Type A	Type A	Type A	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	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	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Improving	Improving	Improving	Improving	Improving	Improving	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving
Integration rule type parameter	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description parameter
Integration rule type criteria	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE
Integration rule description criteria
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
GES extent achieved	17.00	17.00	17.00	17.00	17.00	17.00	17.00	100.00	100.00	100.00	100.00	100.00	100.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	28.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00
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
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 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
Description overall status	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.	The analysis of abundance and breeding productivity suggests that birds foraging at the water surface, birds foraging in the water column, birds feeding on benthos (diving to the seabed) and wading birds (foraging in shallow water or on mudflats) are not doing well. Less than 75% of birds foraging at the water surface, wading birds and birds feeding on benthos, both breeding and non-breeding, are observed in numbers indicative of population stability in the North Sea. Numbers have declined since the mid-2000s for breeding populations and since 1998 for non-breeding populations. In the Belgian part of the North Sea, additional observations at sea revealed population declines for the six observed bird species that forage at the water surface, two of the five species of birds that forage in the water column and the common scoter, a species that feeds on benthos. or the common tern, breeding success at the Zeebrugge colony was even well above the level needed to maintain a stable population. This is a notable exception in the generally low reproductive success of this species in the North Sea, where it is classified as one of the six critically endangered water surface foraging species.
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Related pressures	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence	Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Related targets	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6	D1.1 D1.2 D1.3 D1.4 D1.5 D1.6
Test TV	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA
Test results	False	False	False	False	False	False	False	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	Correct	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False