Art8-2024

Member State report / Art8-2024 / 2024 / D9 / Spain / NE Atlantic: Macaronesia

Report type	Member State report to Commission
MSFD Article	Art8
Report due	2024-10-15
GES Descriptor	D9 Contaminants in seafood
Member State	Spain
Region/subregion	NE Atlantic: Macaronesia
Report date	2026-03-24 07:53:11

AMA-ES-SD-FAO34

Simplified table

Regional assessment area
Component MRUs
GES component	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9
Feature	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood
Element		Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds
Element extent
Trend element		Unknown		Unknown		Unknown		Unknown		Unknown		Stable		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		Stable	Unknown
Element 2		Acanthocybium solandri	Acanthocybium solandri	Balistes capriscus	Balistes capriscus	Canthidermis sufflamen	Canthidermis sufflamen	Heteropriacanthus cruentatus	Heteropriacanthus cruentatus	Katsuwonus pelamis	Katsuwonus pelamis	Sardina pilchardus	Sardina pilchardus	Sarpa salpa	Sarpa salpa	Scomber colias	Scomber colias	Serranus atricauda	Serranus atricauda	Serranus cabrilla	Serranus cabrilla	Sparisoma cretense	Sparisoma cretense	Thunnus albacares	Thunnus albacares	Thunnus obesus	Thunnus obesus	Thunnus thynnus	Thunnus thynnus	Trachurus picturatus	Trachurus picturatus	Acanthocybium solandri	Acanthocybium solandri	Balistes capriscus	Balistes capriscus	Canthidermis sufflamen	Canthidermis sufflamen	Heteropriacanthus cruentatus	Heteropriacanthus cruentatus	Katsuwonus pelamis	Katsuwonus pelamis	Sardina pilchardus	Sardina pilchardus	Sarpa salpa	Sarpa salpa	Scomber colias	Scomber colias	Scomber colias	Serranus atricauda	Serranus atricauda	Serranus cabrilla	Serranus cabrilla	Sparisoma cretense	Sparisoma cretense	Thunnus albacares	Thunnus albacares	Thunnus obesus	Thunnus obesus	Thunnus thynnus	Thunnus thynnus	Trachurus picturatus	Trachurus picturatus	Trachurus picturatus	Trachurus picturatus	Trachurus picturatus	Scomber colias	Scomber colias	Trisopterus minutus	Zeus faber
Element source		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU		EU			EU		EU		EU		EU		EU		EU		EU					EU		EU	EU
Criterion	D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1	D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1		D9C1	D9C1	D9C1	D9C1		D9C1
Parameter			CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle
Threshold value upper			0.05		0.05		0.05		0.05		0.1		0.25		0.05		0.1		0.05		0.05		0.05		0.1		0.1		0.1		0.05		0.3		0.3		0.3		0.3		0.3		0.3		0.3		0.3	0.3		0.3		0.3		0.3		0.3		0.3		0.3		0.3	0.3	0.3	0.3		0.3
Threshold value lower
Threshold value operator			<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=		<=	<=		<=		<=		<=		<=		<=		<=		<=	<=	<=	<=		<=
Threshold qualitative
Threshold value source			National		National		National		National		National		National		National		National		National		National		National		National		National		National		National		National		National		National		National		National		National		National		National	National		National		National		National		National		National		National		National	National	National	National		National
Value achieved upper			0.007		0.08		0.03		0.02		0.014		0.02		0.00723		0.043		0.0045		0.108		0.01		0.009		0.006		0.051		0.021		0.009		0.53		0.37		0.4		0.006		0.0923		0.0323		0.12	0.127		0.03		0.054		0.02		0.012		0.01		0.28		0.04	0.04	0.131	0.29		0.11
Value achieved lower
Value unit			microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight	microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight		microgram per kilogram of wet weight
Proportion threshold value			90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0	90.0		90.0		90.0		90.0		90.0		90.0		90.0		90.0	90.0	90.0	90.0		90.0
Proportion value achieved
Proportion threshold value unit			% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value
Trend parameter			Unknown		Unknown		Unknown		Unknown		Unknown		Stable		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
Parameter achieved			Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown	Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown	Unknown	Unknown	Unknown		Unknown
Description parameter			Media de 15 muestras		Media de 28 muestras		Media de 6 muestras		Media de 20 muestras		Media de 15 muestras		Media de 414 muestras		Media de 30 muestras		Media de 395 muestras		Media de 20 muestras		Media de 20 individuos		Media de 10 muestras		Media de 15 muestras		Media de 15 muestras		Media de 15 muestras		Media de 415 muestras		Media de 15 muestras		Media de 28 muestras		Media de 6 muestras		Media de 20 muestras		Media de 15 muestras		Media de 414 muestras		Media de 30 muestras		Media de 50 muestras	Media de 345 muestras		Media de 20 muestras		Media de 20 muestras		Media de 10 muestras		Media de 15 muestras		Media de 15 muestras		Media de 15 muestras		Media de 31 muestras	Media de 40 muestras	Media de 294 muestras	Media de 50 muestras		Media de 30 muestras
Related indicator			Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota	Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota		Metales en biota	Metales en biota	Metales en biota	Metales en biota		Metales en biota
Criteria status	Good
Description criteria
Element status		Good		Not good		Good		Good		Good		Good		Good		Good		Good		Not good		Good		Good		Good		Good		Good		Good		Not good		Not good		Not good		Good		Good		Good		Good			Good		Good		Good		Good		Good		Good		Good					Good		Good	Good
Description element
Source assessment feature	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Reporting method feature	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D
Trend feature	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Integration rule type parameter	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)	Como valor umbral se propone utilizar el valor umbral del 10%, es decir, para cumplir el BEA es necesario que el 90% de las muestras se encuentre por debajo de la CMP (concentración máxima permitida)
GES extent threshold
GES extent achieved
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status
GES achieved	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Description overall status	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison	we cannot say as we do not have data for all compounds family, neither we have a trend feature for comparison
Assessments period	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021
Related pressures	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9	B.22 B.3 B.4 B.8 C.11 C.14 C.15 C.17 C.18 C.19 C.9
Test TV	NA	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	No	NA	No	NA	No	NA	Yes	NA	Yes	NA	Yes	NA	Yes	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	Yes	Yes	Yes	NA	Yes	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	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