MS/Art8-2024/2024/D9/Spain/Mediterranean: Western Mediterranean Sea

Member State report / Art8-2024 / 2024 / D9 / Spain / Mediterranean: Western Mediterranean Sea

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	Mediterranean: Western Mediterranean Sea
Report date	2026-03-24 07:53:11

MWE-ES-SD-FAO37

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	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	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	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	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)
Element extent
Trend element		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Deteriorating		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Stable		Unknown		Unknown		Unknown		Stable		Stable		Deteriorating		Unknown		Stable		Stable		Stable		Stable		Unknown		Stable		Unknown		Stable		Unknown		Stable		Unknown		Deteriorating		Unknown		Unknown		Stable		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Stable		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Deteriorating			Unknown			Stable		Stable
Element 2		Auxis rochei rochei	Auxis rochei rochei	Merluccius merluccius	Merluccius merluccius	Mullus surmuletus	Mullus surmuletus	Scomber japonicus	Scomber japonicus	Auxis rochei rochei	Auxis rochei rochei	Merluccius merluccius	Merluccius merluccius	Mullus surmuletus	Mullus surmuletus	Scomber japonicus	Scomber japonicus	Aphia minuta	Aphia minuta	Aristeus antennatus	Aristeus antennatus	Cepola macrophthalma	Cepola macrophthalma	Chelidonichthys lucerna	Chelidonichthys lucerna	Conger conger	Conger conger	Coryphaena hippurus	Coryphaena hippurus	Dentex dentex	Dentex dentex	Diplodus sargus sargus	Diplodus sargus sargus	Engraulis encrasicolus	Engraulis encrasicolus	Epinephelus marginatus	Epinephelus marginatus	Labrus bimaculatus	Labrus bimaculatus	Lamna nasus	Lamna nasus	Lepidorhombus boscii	Lepidorhombus boscii	Lepidorhombus whiffiagonis	Lepidorhombus whiffiagonis	Loligo vulgaris	Loligo vulgaris	Lophius piscatorius	Lophius piscatorius	Merluccius merluccius	Merluccius merluccius	Micromesistius poutassou	Micromesistius poutassou	Mullus barbatus	Mullus barbatus	Mullus surmuletus	Mullus surmuletus	Muraena helena	Muraena helena	Mytilus galloprovincialis	Mytilus galloprovincialis	Nephrops norvegicus	Nephrops norvegicus	Pagellus acarne	Pagellus acarne	Pagellus bogaraveo	Pagellus bogaraveo	Pagellus erythrinus	Pagellus erythrinus	Pagrus pagrus	Pagrus pagrus	Phycis blennoides	Phycis blennoides	Pontinus kuhlii	Pontinus kuhlii	Raja clavata	Raja clavata	Sardina pilchardus	Sardina pilchardus	Sardinella albella	Sardinella albella	Sardinella aurita	Sardinella aurita	Sciaena umbra	Sciaena umbra	Scorpaena porcus	Scorpaena porcus	Scorpaena scrofa	Scorpaena scrofa	Scyliorhinus canicula	Scyliorhinus canicula	Sepia officinalis	Sepia officinalis	Seriola dumerili	Seriola dumerili	Serranus cabrilla	Serranus cabrilla	Serranus scriba	Serranus scriba	Solea solea	Solea solea	Sparus aurata	Sparus aurata	Sphyraena sphyraena	Sphyraena sphyraena	Spicara smaris	Spicara smaris	Spondyliosoma cantharus	Spondyliosoma cantharus	Trachinus draco	Trachinus draco	Trachurus trachurus	Trachurus trachurus	Trisopterus minutus	Xyrichtys novacula	Xyrichtys novacula	Zeus faber	Engraulis encrasicolus	Engraulis encrasicolus	Sarda sarda	Sarda sarda
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		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		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		Concentration in biota		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		Concentration in biota		CONC-B-Muscle		CONC-B-Muscle		Concentration in biota		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		Concentration in biota		Concentration in biota		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		Concentration in biota		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		Concentration in biota	CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle
Threshold value upper			0.15		0.05		0.05		0.1		0.3		0.3		0.3		0.3		0.5		0.5		0.5		0.5		0.5		0.5		0.5		0.5		0.3		0.5		0.5		1.0		1.0		0.5		0.3		0.5		0.5		0.5		1.0		1.0		0.5		0.5		0.5		1.0		1.0		1.0		0.5		0.5		0.5		0.5		0.3		0.5		0.5		0.5		0.5		0.5		1.0		0.3		0.5		0.5		0.5		0.5		0.5		0.5		0.5		0.5		0.5		0.5	1.0		0.5	0.5		75.0		75.0
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		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			0.18		0.01		0.02		0.01		0.45		0.05		0.05		0.2		0.09		0.34		0.025		0.27		0.46		0.067		0.68		0.23		0.06		0.6		0.29		3.0		0.38		0.13		0.12		0.59		0.27		0.11		0.14		0.19		0.43		0.07		0.756		0.28		0.19		0.27		0.23		0.25		0.11		1.88		0.097		0.17		0.11		0.14		0.155		0.25		0.31		0.06		0.13		0.22		0.27		0.35		0.09		1.0		0.12		0.22		0.102		0.21	0.23		0.11	0.24		51.0		51.0
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		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		milligram per kilogram of wet weight		milligram 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		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		% 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		Unknown		Unknown		Unknown		Unknown		Stable		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Stable		Unknown		Unknown		Unknown		Stable		Stable		Deteriorating		Unknown		Stable		Stable		Stable		Stable		Unknown		Stable		Unknown		Stable		Unknown		Stable		Unknown		Stable		Unknown		Unknown		Stable		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Stable		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Deteriorating	Stable		Unknown	Unknown		Stable		Stable
Parameter achieved			Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Yes		Yes		Yes		Yes		Yes		Yes		No		Yes		Yes		No		Yes		No		Yes		Yes		Yes		No		Yes		Yes		Yes		Yes		Yes		Yes		No		Yes		Yes		Yes		Yes		Yes		Yes		No		Yes		Yes		Yes		Yes		Yes		Yes		Yes		Yes		Yes		Yes		Yes		Yes		Yes		No		Yes		Yes		Yes		Yes	Yes		Yes	Yes		Yes		Yes
Description parameter			Media de 5 muestras		Media de 5 muestras		Media de 5 muestras		Media de 5 muestras		Media de 5 muestras		Media de 5 muestras		Media de 5 muestras		Media de 5 muestras		Valor individual		Media de 9 muestras		Media de 2 muestras		Media de 4 muestras		Media de 39 muestras		Media de 2 muestras		Media de 17 muestras		Media de 20 muestras		Media de 7 muestras		Media de 24 muestras		Valor individual		Valor individual		Valor individual		Media de 10 muestras		Media de 9 muestras		Media de 41 muestras		Media de 29 muestras		Media de 5 muestras		Media de 11 muestras		Media de 13 muestras		Media de 28 muestras		Valor individual		Media de 2 muestras		Media de 11 muestras		Media de 3 muestras		Media de 18 muestras		Media de 9 muestras		Media de 6 muestras		Media de 5 muestras		Media de 2 muestras		Media de 9 muestras		Media de 2 muestras		Valor individual		Media de 4 muestras		Media de 2 muestras		Media de 29 muestras		Media de 16 muestras		Media de 9 muestras		Media de 10 muestras		Media de 10 muestras		Media de 10 muestras		Media de 15 muestras		Media de 4 muestras		Valor individual		Media de 2 muestras		Media de 12 muestras		Media de 4 muestras		Media de 14 muestras	Media de 12 muestras		Media de 2 muestras	Media de 15 muestras		Valor individual		Valor individual
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		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		PCBs en biota		PCBs en biota
Criteria status	Not good
Description criteria
Element status		Not good		Good		Good		Good		Not good		Good		Good		Good		Good		Not good		Good		Not good		Not good		Good		Not good		Good		Good		Not good		Good		Not good		Good		Good		Not good		Not good		Not good		Good		Good		Good		Not good		Good		Not good		Good		Good		Good		Good		Not good		Good		Not good		Good		Good		Good		Good		Good		Good		Not good		Good		Not good		Good		Good		Not good		Good		Not good		Good		Not 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	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	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	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	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	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	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)	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	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	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	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	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	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	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	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	No	NA	Yes	NA	Yes	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	No	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	Yes	NA	No	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	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	Yes	NA	Yes	Yes	NA	Yes	Yes	NA	Yes	NA	Yes
Test results	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	Correct	False	Correct	Correct	False	Correct	False	Correct