Member State report / Art8-2024 / 2024 / D9 / Portugal / NE Atlantic: Bay of Biscay & Iberian Coast
| Report type | Member State report to Commission |
| MSFD Article | Art8 |
| Report due | 2024-10-15 |
| GES Descriptor | D9 Contaminants in seafood |
| Member State | Portugal |
| Region/subregion | NE Atlantic: Bay of Biscay & Iberian Coast |
| Report date | 2026-01-14 17:07:17 |
Part of territorial continental waters (ABI-PT-AA-CONT_AT)
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
|
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
|
Element |
Benzo(a)pyrene |
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 |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
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 |
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) |
PFOA |
PFOA |
PFOS |
PFOS |
Perfluorohexane sulfonate (PFHxS) |
Perfluorohexane sulfonate (PFHxS) |
Perfluorononanoate (PFNA) |
Perfluorononanoate (PFNA) |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Element extent |
|||||||||||||||||||||||||||||||||||||
Trend element |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Element 2 |
Mytilus spp.
|
Engraulis encrasicolus
|
Glycymeris glycymeris
|
Mytilus spp.
|
Paracentratus lividus
|
Patella spp.
|
Raja brachyura
|
Sardina pilchardus
|
Spisula solida
|
Engraulis encrasicolus
|
Glycymeris glycymeris
|
Mytilus spp
|
Paracentratus lividus
|
Patella spp
|
Raja brachyura
|
Sardina pilchardus
|
Spisula solida
|
Glycymeris glycymeris
|
Mytilus spp.
|
Paracentratus lividus
|
Patella spp.
|
Raja brachyura
|
Spisula solida
|
Mytillus spp.
|
Spisula solida
|
Spisula solida
|
Trachurus trachurus
|
Spisula solida
|
Trachurus trachurus
|
Spisula solida
|
Trachurus trachurus
|
Spisula solida
|
Trachurus trachurus
|
Mytillus spp.
|
Spisula solida
|
Mytillus spp.
|
|
Element source |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Criterion |
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
|
Parameter |
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Other
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Other
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Other
|
Concentration in biota
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
|
Threshold value upper |
5.0 |
0.25 |
1.0 |
1.0 |
1.0 |
1.0 |
0.05 |
0.25 |
1.0 |
0.3 |
1.5 |
1.5 |
1.5 |
1.5 |
0.3 |
0.3 |
1.5 |
0.5 |
0.5 |
0.5 |
0.3 |
0.5 |
0.5 |
75.0 |
75.0 |
0.7 |
1.0 |
3.0 |
7.0 |
1.5 |
0.2 |
1.0 |
2.5 |
30.0 |
30.0 |
3.5 |
|
Threshold value lower |
|||||||||||||||||||||||||||||||||||||
Threshold value operator |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
|
Threshold qualitative |
|||||||||||||||||||||||||||||||||||||
Threshold value source |
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
|
Value achieved upper |
0.7 |
0.21 |
0.1 |
0.8 |
0.007 |
0.13 |
0.41 |
0.17 |
0.003 |
0.32 |
0.014 |
0.13 |
0.005 |
0.016 |
0.014 |
0.012 |
0.013 |
||||||||||||||||||||
Value achieved lower |
|||||||||||||||||||||||||||||||||||||
Value unit |
microgram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
ng/g
|
ng/g
|
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
|
ug/kg
|
ug/kg
|
pg TEQ/g ww
|
|
Proportion threshold value |
|||||||||||||||||||||||||||||||||||||
Proportion value achieved |
|||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
|||||||||||||||||||||||||||||||||||||
Trend parameter |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
|
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
|
Description parameter |
< 1 (LQ)
|
|
Mediana: 0.70
Percentil 90: 1.0
|
Mediana: 0.21
Percentil 90: 0.31
|
Mediana: 0.10
Percentil 90: 0.13
|
Mediana: 0.80
Percentil 90: 1.7
|
|
Mediana: 0.007
Percentil 90: 0.013
|
Mediana: 0.13
Percentil 90: 0.18
|
|
Mediana: 0.41
Percentil 90: 0.75
|
Mediana: 0.17
Percentil 90: 0.23
|
Mediana: 0.03
Percentil 90: 0.07
|
Mediana: 0.32
Percentil 90: 0.49
|
|
Mediana: 0.014
Percentil 90: 0.036
|
Mediana: 0.13
Percentil 90: 0.27
|
Mediana: 0.005
Percentil 90: 0.014
|
Mediana: 0.016
Percentil 90: 0.022
|
Mediana: 0.014
Percentil 90: 0.022
|
Mediana: 0.012
Percentil 90: 0.019
|
< limiar
|
Mediana: 0.013
Percentil 90: 0.022
|
|
|
< 0,1 (LQ)
|
< 0,1 (LQ)
|
< 0,5 (LQ)
|
< 0,5 (LQ)
|
< 0,1 (LQ)
|
< 0,1 (LQ)
|
< 0,5 (LQ)
|
< 0,5 (LQ)
|
|
|
Concentrações máximas e medianas (ng OMS-TEQ/kg):
Moledo - 3.00 (2.90)
Norte - 3.40 (2.75)
Cabo do Mundo - 3.40 (3.00)
Aguda - 3.60 (3.10)
Tamargueira - 3.20 (2.80)
|
|
Related indicator |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Criteria status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
|
Description criteria |
|||||||||||||||||||||||||||||||||||||
Element status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Description element |
Mytillys spp.
|
||||||||||||||||||||||||||||||||||||
Source assessment feature |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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 |
Trend feature |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
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
|
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
|
Integration rule description criteria |
|||||||||||||||||||||||||||||||||||||
GES extent threshold |
|||||||||||||||||||||||||||||||||||||
GES extent achieved |
|||||||||||||||||||||||||||||||||||||
GES extent unit |
|||||||||||||||||||||||||||||||||||||
GES achieved |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
Description overall status |
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
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 |
Related pressures |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|||||||||||||||||||||||||||||||||||||
Test TV |
NA |
NA |
Yes |
Yes |
Yes |
Yes |
NA |
Yes |
Yes |
NA |
NA |
Yes |
Yes |
Yes |
Yes |
NA |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
NA |
Yes |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
Test results |
False |
False |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
False |
False |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
Part of territorial continental waters (ABI-PT-AA-CONT_CT)
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
|
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
|
Element |
Benzo(a)pyrene |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
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 |
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) |
PFOA |
PFOS |
Perfluorohexane sulfonate (PFHxS) |
Perfluorononanoate (PFNA) |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Element extent |
||||||||||||||||||||||||
Trend element |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Element 2 |
Mytilus spp.
|
Bolinus brandaris
|
Charonia rubicunda
|
Donax trunculus
|
Sardina pilchardus
|
Scomber colias
|
Bolinus brandaris
|
Charonia rubicunda
|
Donax trunculus
|
Sardina pilchardus
|
Scomber colias
|
Bolinus brandaris
|
Charonia rubicunda
|
Donax trunculus
|
Sardina pilchardus
|
Scomber colias
|
Donax trunculus
|
Spisula solida
|
Spisula solida
|
Spisula solida
|
Spisula solida
|
Donax trunculus
|
Mytillus spp.
|
|
Element source |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Criterion |
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
|||
Parameter |
Concentration in biota
|
Concentration in biota
|
CONC-B-Other
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Other
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Other
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
|||
Threshold value upper |
5.0 |
1.0 |
1.0 |
1.0 |
0.25 |
0.1 |
1.5 |
1.5 |
1.5 |
0.3 |
0.3 |
0.3 |
0.3 |
0.5 |
75.0 |
0.7 |
3.0 |
1.5 |
1.0 |
30.0 |
3.5 |
|||
Threshold value lower |
||||||||||||||||||||||||
Threshold value operator |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
|||
Threshold qualitative |
||||||||||||||||||||||||
Threshold value source |
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
|||
Value achieved upper |
0.7 |
0.012 |
0.013 |
0.004 |
0.008 |
0.19 |
0.04 |
0.12 |
0.016 |
0.009 |
0.041 |
0.09 |
0.018 |
|||||||||||
Value achieved lower |
||||||||||||||||||||||||
Value unit |
ug/g ww
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
ng/g
|
microgram per kilogram of wet weight
|
microgram per kilogram of wet weight
|
microgram per kilogram of wet weight
|
microgram per kilogram of wet weight
|
ug/kg
|
pg TEQ/g ww
|
|||
Proportion threshold value |
||||||||||||||||||||||||
Proportion value achieved |
||||||||||||||||||||||||
Proportion threshold value unit |
||||||||||||||||||||||||
Trend parameter |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
|||
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Unknown |
Yes |
Yes |
Yes |
Yes |
|||
Description parameter |
< 1 (LQ)
|
Mediana: 0.7
Percentil 90: 3.6
|
Mediana: 0.012
Percentil 90: 0.210
|
Mediana: 0.013
Percentil 90: 0.022
|
Mediana: 0.004
Percentil 90: 0.012
|
Mediana: 0.008
Percentil 90: 0.026
|
Mediana: 0.19
Percentil 90: 0.25
|
Mediana: 0.04
Percentil 90: 0.50
|
Mediana: 0.12
Percentil 90: 0.21
|
Mediana: 0.016
Percentil 90: 0.037
|
Mediana: 0.009
Percentil 90: 0.014
|
Mediana: 0.041
Percentil 90: 0.100
|
Mediana: 0.09
Percentil 90: 0.17
|
Mediana: 0.018
Percentil 90: 0.025
|
|
< 0,1 (LQ)
|
A substância foi detetada mas não quantificada
|
< 0,1 (LQ)
|
< 0,5 (LQ)
|
|
Concentração máxima e mediana (ng OMS-TEQ/kg):
Santo António: 3,40 (3,20)
|
|||
Related indicator |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||
Criteria status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Unknown |
Good |
Good |
Good |
Good |
|||
Description criteria |
||||||||||||||||||||||||
Element status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Unknown |
Good |
Good |
Good |
Good |
Description element |
Mytillus spp.
|
|||||||||||||||||||||||
Source assessment feature |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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 |
Trend feature |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
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
|
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
|
Integration rule description criteria |
||||||||||||||||||||||||
GES extent threshold |
||||||||||||||||||||||||
GES extent achieved |
||||||||||||||||||||||||
GES extent unit |
||||||||||||||||||||||||
GES achieved |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
Description overall status |
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
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 |
Related pressures |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Test TV |
NA |
Yes |
Yes |
Yes |
Yes |
Yes |
NA |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
Test results |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
False |
Correct |
False |
False |
False |
False |
Sub Part of territorial continental waters (ABI-PT-AA-CONT_D9BT1.1)
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
|
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
|
Element |
Benzo(a)pyrene |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Mercury and its compounds |
Mercury and its compounds |
Mercury and its compounds |
Mercury and its compounds |
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) |
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) |
PFOA |
PFOA |
PFOA |
PFOA |
PFOS |
PFOS |
PFOS |
PFOS |
Perfluorohexane sulfonate (PFHxS) |
Perfluorohexane sulfonate (PFHxS) |
Perfluorohexane sulfonate (PFHxS) |
Perfluorohexane sulfonate (PFHxS) |
Perfluorononanoate (PFNA) |
Perfluorononanoate (PFNA) |
Perfluorononanoate (PFNA) |
Perfluorononanoate (PFNA) |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Element extent |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend element |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Element 2 |
Mytilus spp.
|
Callista chione
|
Chelidonichthys cuculus
|
Donax trunculus
|
Lepidorhombus boscii
|
Lepidotrigla cavillone
|
Merluccius merluccius
|
Mytilus spp.
|
Octopus vulgaris
|
Paracentratus lividus
|
Patella spp.
|
Raja spp.
|
Scomber colias
|
Scorpaena porcus
|
Sepia officinalis
|
Solea solea
|
Solen marginatus
|
Spisula solida
|
Callista chione
|
Chelidonichthys cuculus
|
Donax trunculus
|
Lepidorhombus boscii
|
Lepidotrigla cavillone
|
Merluccius merluccius
|
Mytilus spp
|
Octopus vulgaris
|
Paracentratus lividus
|
Patella spp
|
Raja spp.
|
Scomber colias
|
Scorpaena porcus
|
Sepia officinalis
|
Solea solea
|
Solen marginatus
|
Spisula solida
|
Callista chione
|
Donax trunculus
|
Mytilus spp.
|
Octopus vulgaris
|
Paracentratus lividus
|
Patella spp.
|
Raja spp.
|
Sepia officinalis
|
Solen marginatus
|
Spisula solida
|
Callista chione
|
Donax trunculus
|
Mytillus spp.
|
Solen marginatus
|
Spisula solida
|
Microchirus variegatus
|
Solea solea
|
Spisula solida
|
Trachurus trachurus
|
Microchirus variegatus
|
Solea solea
|
Spisula solida
|
Trachurus trachurus
|
Microchirus variegatus
|
Solea solea
|
Spisula solida
|
Trachurus trachurus
|
Microchirus variegatus
|
Solea solea
|
Spisula solida
|
Trachurus trachurus
|
Callista chione
|
Donax trunculus
|
Mytillus spp.
|
Solen marginatus
|
Spisula solida
|
Mytillus spp.
|
|
Element source |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
|
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
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
|
Parameter |
Concentration in biota
|
Concentration in biota
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Other
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Other
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Muscle
|
Other
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
|
Threshold value upper |
5.0 |
1.0 |
0.05 |
1.0 |
0.05 |
0.05 |
0.05 |
1.0 |
1.0 |
1.0 |
1.0 |
0.05 |
0.1 |
0.05 |
1.0 |
0.05 |
1.0 |
1.0 |
1.5 |
0.3 |
1.5 |
0.3 |
0.3 |
0.3 |
1.5 |
0.3 |
1.5 |
1.5 |
0.3 |
0.3 |
0.3 |
0.3 |
0.3 |
1.5 |
1.5 |
0.5 |
0.5 |
0.5 |
0.3 |
0.5 |
0.3 |
0.5 |
0.3 |
0.5 |
0.5 |
75.0 |
75.0 |
75.0 |
75.0 |
75.0 |
0.2 |
0.2 |
0.7 |
1.0 |
2.0 |
2.0 |
3.0 |
7.0 |
0.2 |
0.2 |
1.5 |
0.2 |
0.5 |
0.5 |
1.0 |
2.5 |
30.0 |
30.0 |
30.0 |
30.0 |
30.0 |
3.5 |
|
Threshold value lower |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value operator |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
|
Threshold qualitative |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value source |
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
|||
Value achieved upper |
0.15 |
0.024 |
0.16 |
0.008 |
0.16 |
1.6 |
0.005 |
0.003 |
0.05 |
0.1 |
0.09 |
0.013 |
0.007 |
0.012 |
0.26 |
0.005 |
0.08 |
0.17 |
0.003 |
0.047 |
0.003 |
0.055 |
0.09 |
0.09 |
0.005 |
0.017 |
0.017 |
0.031 |
0.012 |
0.012 |
0.046 |
0.015 |
0.014 |
||||||||||||||||||||||||||||||||||||||||
Value achieved lower |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Value unit |
microgram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
ng/g
|
ng/g
|
ng/g
|
ng/g
|
ng/g
|
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
|
ug/g ww
|
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
|
ug/kg
|
ug/kg
|
ug/kg
|
ug/kg
|
ug/kg
|
pg TEQ/g ww
|
|
Proportion threshold value |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion value achieved |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend parameter |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
|
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Unknown |
Unknown |
Unknown |
Unknown |
Yes |
Yes |
Yes |
Unknown |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
|
Description parameter |
< LQ (1)
|
Mediana: 0.15
Percentil 90: 0.17
|
|
Mediana: 0.024
Percentil 90: 0.05
|
|
|
|
Mediana: 0.16
Percentil 90: 0.27
|
Mediana: 0.008
Percentil 90: 0.014
|
Mediana: 0.16
Percentil 90: 0.27
|
Mediana: 1.6
Percentil 90: 3.1
|
|
Mediana: 0.005
Percentil 90: 0.008
|
|
Mediana: 0.003
Percentil 90: 0.005
|
|
Mediana: 0.05
Percentil 90: 0.08
|
Mediana: 0.10
Percentil 90: 0.70
|
Mediana: 0.009
Percentil 90: 0.12
|
|
Mediana: 0.013
Percentil 90: 0.26
|
Mediana: 0.007
Percentil 90: 0.045
|
|
Mediana: 0.012
Percentil 90: 0.043
|
Mediana: 0.26
Percentil 90: 0.55
|
Mediana: 0.005
Percentil 90: 0.008
|
Mediana: 0.08
Percentil 90: 0.48
|
Mediana: 0.17
Percentil 90: 0.27
|
|
Mediana: 0.003
Percentil 90: 0.004
|
Mediana: 0.047
Percentil 90: 0.067
|
Mediana: 0.003
Percentil 90: 0.005
|
Mediana: 0.055
Percentil 90: 0.088
|
Mediana: 0.09
Percentil 90: 0.13
|
Mediana: 0.09
Percentil 90: 0.19
|
Mediana: 0.005
Percentil 90: 0.013
|
Mediana: 0.017
Percentil 90: 0.026
|
Mediana: 0.017
Percentil 90: 0.026
|
Mediana: 0.031
Percentil 90: 0.041
|
Mediana: 0.012
Percentil 90: 0.013
|
Mediana: 0.012
Percentil 90: 0.017
|
< limiar
|
Mediana: 0.046
Percentil 90: 0.077
|
Mediana: 0.015
Percentil 90: 0.024
|
Mediana: 0.014
Percentil 90: 0.031
|
|
|
|
|
|
< 0,1 (LQ)
|
< 0,1 (LQ)
|
< 0,1 (LQ)
|
< LQ (0,1)
|
A substância foi detetada mas não quantificada
|
A substância foi detetada mas não quantificada
|
A substância foi detetada mas não quantificada
|
A substância foi detetada mas não quantificada
|
< 0,1 (LQ)
|
< 0,1 (LQ)
|
< 0,1 (LQ)
|
A substância foi detetada mas não quantificada
|
< 0,5 (LQ)
|
< 0,5 (LQ)
|
< 0,5 (LQ)
|
< 0,5 (LQ)
|
|
|
|
|
|
Concentração máxima e mediana (ng OMS-TEQ/kg):
Coxos: 2,60 (2,50)
|
|
Related indicator |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Criteria status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Unknown |
Unknown |
Unknown |
Unknown |
Good |
Good |
Good |
Unknown |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
|
Description criteria |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Element status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Unknown |
Unknown |
Unknown |
Unknown |
Good |
Good |
Good |
Unknown |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Description element |
Mytillys spp.
|
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Source assessment feature |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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 |
Trend feature |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
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
|
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
|
Integration rule description criteria |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent threshold |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent achieved |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent unit |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES achieved |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
Description overall status |
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
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 |
Related pressures |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Test TV |
NA |
Yes |
NA |
Yes |
NA |
NA |
NA |
Yes |
Yes |
Yes |
No |
NA |
Yes |
NA |
Yes |
NA |
Yes |
Yes |
NA |
Yes |
NA |
Yes |
Yes |
NA |
Yes |
Yes |
Yes |
Yes |
Yes |
NA |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
NA |
Yes |
Yes |
Yes |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
Test results |
False |
Correct |
False |
Correct |
False |
False |
False |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
Correct |
False |
Correct |
Correct |
False |
Correct |
False |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
False |
False |
False |
False |
False |
False |
False |
False |
False |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
Correct |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
Sub Part of territorial continental waters (ABI-PT-AA-CONT_D9BT1.2)
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
|
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
|
Element |
Benzo(a)pyrene |
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 |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
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 |
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) |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Element extent |
||||||||||||||||||||||||||
Trend element |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Element 2 |
Mytilus spp.
|
Magallana gigas
|
Mytilus spp.
|
Ostrea edulis
|
Paracentratus lividus
|
Patella spp.
|
Sardina pilchardus
|
Scomber colias
|
Magallana gigas
|
Mytilus spp
|
Ostrea edulis
|
Paracentratus lividus
|
Patella spp
|
Sardina pilchardus
|
Scomber colias
|
Magallana gigas
|
Mytilus edulis
|
Ostrea edulis
|
Paracentratus lividus
|
Patella spp.
|
Mytillus spp.
|
Spisula solida
|
Mytillus spp.
|
Solen marginatus
|
Mytillus spp.
|
|
Element source |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
Foodstuffs |
|
Criterion |
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
|||
Parameter |
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Other
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Other
|
Concentration in biota
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
CONC-B-Other
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
|||
Threshold value upper |
5.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
0.25 |
1.0 |
1.5 |
1.5 |
1.5 |
1.5 |
1.5 |
0.3 |
0.3 |
0.5 |
0.5 |
0.5 |
0.3 |
75.0 |
75.0 |
30.0 |
3.5 |
|||
Threshold value lower |
||||||||||||||||||||||||||
Threshold value operator |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
<= |
|||
Threshold qualitative |
||||||||||||||||||||||||||
Threshold value source |
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
Regulation on contaminants in foodstuffs (EC 1881/2006)
|
|||
Value achieved upper |
0.7 |
0.24 |
1.0 |
0.19 |
1.4 |
0.004 |
0.009 |
0.12 |
0.15 |
0.08 |
0.03 |
0.27 |
0.015 |
0.005 |
0.005 |
0.016 |
0.005 |
0.011 |
||||||||
Value achieved lower |
||||||||||||||||||||||||||
Value unit |
microgram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
ng/g
|
ng/g
|
ug/kg
|
pg TEQ/g ww
|
|||
Proportion threshold value |
||||||||||||||||||||||||||
Proportion value achieved |
||||||||||||||||||||||||||
Proportion threshold value unit |
||||||||||||||||||||||||||
Trend parameter |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
|||
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
|||
Description parameter |
< LQ (1)
|
Mediana: 0.7
Percentil 90: 1.1
|
Mediana: 0.24
Percentil 90: 0.50
|
Mediana: 1.0
Percentil 90: 1.2
|
Mediana: 0.19
Percentil 90: 0.35
|
Mediana: 1.4
Percentil 90: 2.2
|
Mediana: 0.004
Percentil 90: 0.007
|
Mediana: 0.009
Percentil 90: 0.019
|
Mediana: 0.12
Percentil 90: 0.20
|
Mediana: 0.15
Percentil 90: 0.24
|
Mediana: 0.08
Percentil 90: 0.13
|
Mediana: 0.03
Percentil 90: 0.23
|
Mediana: 0.27
Percentil 90: 0.44
|
Mediana: 0.015
Percentil 90: 0.030
|
Mediana: 0.005
Percentil 90: 0.011
|
Mediana: 0.005
Percentil 90: 0.016
|
Mediana: 0.016
Percentil 90: 0.027
|
Mediana: 0.005
Percentil 90: 0.012
|
Mediana: 0.011
Percentil 90: 0.016
|
|
|
|
Concentrações máximas e medianas (ng OMS-TEQ/kg):
Zambujeira do Mar - 3.10 (2.75)
Zavial - 3.40 (3.00)
|
|||
Related indicator |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||
Criteria status |
Good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
|||
Description criteria |
||||||||||||||||||||||||||
Element status |
Good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Description element |
Mytillus spp.
|
|||||||||||||||||||||||||
Source assessment feature |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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 |
Trend feature |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
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
|
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
|
Integration rule description criteria |
||||||||||||||||||||||||||
GES extent threshold |
||||||||||||||||||||||||||
GES extent achieved |
||||||||||||||||||||||||||
GES extent unit |
||||||||||||||||||||||||||
GES achieved |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
GES achieved by 2012 |
Description overall status |
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
Todas as espécies (à exceção da Patella spp.) apresentaram níveis máximos de concentração dos contaminantes inferiores aos limitares.
|
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 |
Related pressures |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Test TV |
NA |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
NA |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
NA |
Yes |
Yes |
Yes |
NA |
NA |
NA |
NA |
NA |
Test results |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
False |
False |
False |
False |
False |