Member State report / Art8 / 2018 / D9 / France / NE Atlantic: Greater North Sea

Report type Member State report to Commission
MSFD Article Art. 8 Initial assessment (and Art. 17 updates)
Report due 2018-10-15
GES Descriptor D9 Contaminants in seafood
Member State France
Region/subregion NE Atlantic: Greater North Sea
Reported by Ministère de la transition Ecologique et Solidaire
Report date 2020-02-19
Report access ART8_GES_FR_2020-02-17.xml

Manche mer du Nord (ANS-FR-MS-MMN)

GES component
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
Element
Benzo(a)pyrene
Cadmium and its compounds
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)
Domoic acid (ASP)
Lead and its compounds
Lipophilic toxins (Okadaic acid, Dinophysistoxins, pectenotoxins, Azaspiracids, Yessotoxins)
Mercury and its compounds
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)
Saxitoxins (PSP)
Sum of PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Indeno(1,2,3-cd)pyrene)
Total dioxins and furans (PCDD + PCDF)
Element code
CAS_50-32-8
CAS_7440-43-9
EEA_33-58-9
3092
CAS_7439-92-1
TOLI
CAS_7439-97-6
SCB6
7551 / CAS_35523-89-8
EEA_33-62-5
EEA_33-40-9
Element code source
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Link to other vocabulary or code lists that may be relevant
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Link to other vocabulary or code lists that may be relevant
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
ICES
Link to other vocabulary or code lists that may be relevant
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Element 2
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Bivalve molluscs
Commercially exploited fish and shellfish
Bivalve molluscs
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Bivalve molluscs
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Element 2 code
PRODPECH
PRODPECH
PRODPECH
BIV
PRODPECH
BIV
PRODPECH
PRODPECH
BIV
PRODPECH
PRODPECH
Element 2 code source
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Element source
EU
EU
EU
National
EU
National
EU
EU
National
EU
EU
Criterion
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
Parameter
Concentration in biota
Concentration in biota
Concentration in biota
Concentration in biota
Concentration in biota
Concentration in biota
Concentration in biota
Concentration in biota
Concentration in biota
Concentration in biota
Concentration in biota
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
For each fishery product concerned, health thresholds set by Regulation 1881/2006/EC as amended on 01/04/2016.
For each fishery product concerned, health thresholds set by Regulation 1881/2006/EC as amended on 01/04/2016.
For each fishery product concerned, health thresholds set by Regulation 1881/2006/EC as amended on 01/04/2016.
Health threshold set for bivalve molluscs by Regulation 853/2004/EC in its amended version of 16/08/2013: For domoic acid (toxins with ASP effect): 20 mg/kg fresh weight
For each fishery product concerned, health thresholds set by Regulation 1881/2006/EC as amended on 01/04/2016.
Health thresholds for bivalve molluscs: Okadaic acid (AO), dinophysistoxins, pectenotoxins: 160 µg AO eq/kg wet weight (w.f.)Azaspiracids (AZA): 160 µg AZA eq/kg w.f. Yessotoxins (YTX): 3750 µg YTX eq/kg w.f.
For each fishery product concerned, health thresholds set by Regulation 1881/2006/EC as amended on 01/04/2016.
For each fishery product concerned, health thresholds set by Regulation 1881/2006/EC as amended on 01/04/2016.
Health threshold set for bivalve molluscs by Regulation 853/2004/EC as amended on 16/08/2013: For saxitoxins (PSP effect toxins): 800 µg/kg fresh weight
For each fishery product concerned, health thresholds set by Regulation 1881/2006/EC as amended on 01/04/2016.
For each fishery product concerned, health thresholds set by Regulation 1881/2006/EC as amended on 01/04/2016.
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)
Other (specify)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Other (specify)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Other (specify)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Threshold value source other
Regulation laying down specific hygiene rules for food of animal origin (EC 853/2004)
Regulation laying down specific hygiene rules for food of animal origin (EC 853/2004)
Regulation laying down specific hygiene rules for food of animal origin (EC 853/2004)
Value achieved upper
Value achieved lower
Value unit
microgram per kilogram of wet weight
microgram per kilogram of wet weight
picogram per gram of wet weight
milligram per kilogram of wet weight
microgram per kilogram of wet weight
Other
microgram per kilogram of wet weight
Other
microgram per kilogram of wet weight
microgram per kilogram of wet weight
picogram per gram of wet weight
Value unit other
µg eq./kg ww
ng/kg ww
Proportion threshold value
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Proportion value achieved
98.2
99.5
98.9
88.0
100.0
98.0
99.5
98.9
100.0
95.0
100.0
Proportion threshold value unit
% of samples achieving threshold value
% of samples achieving threshold value
% of samples achieving threshold value
% of samples achieving threshold value
% of samples achieving threshold value
% of samples achieving threshold value
% of samples achieving threshold value
% of samples achieving threshold value
% of samples achieving threshold value
% of samples achieving threshold value
% of samples achieving threshold value
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
No
No
No
No
Yes
No
No
No
Yes
No
Yes
Description parameter
Benzo(a)pyrene analyses also result in a percentage of exceedances above the threshold, set at 0% in this assessment. However, the % exceedance remains lower (1.8%) than that observed for ∑4HAP. The parameter is not met for benzo(a)pyrene.
Cadmium concentrations show some exceedances of the regulatory limit for one sample from the mollusc group (out of a total of 146 samples) and two samples from the crustacean group (out of a total of 29 samples). The other three groups (cephalopods, most consumed fish and predatory fish) showed no exceedance of the regulatory maximum limit. The percentage of exceedances is low overall but still above the threshold, set at 0 % for this assessment. The parameter is therefore not reached for cadmium.
PCDD/F + PCB-DL concentrations show some exceedances of the regulatory limit for one sample from the mollusc group (out of a total of 179 samples), four samples from the most consumed fish group (out of a total of 184 samples) and two samples from the bivalve mollusc group. The percentage of exceedances is overall low but still above the threshold set at 0 % for this assessment. The parameter is therefore not reached for PCDD/F + PCB-DL.
The parameter is not reached for ASP toxins. ASP toxins are only found in scallops, and exceed the regulatory threshold of 20 mg.kg-1 in 18% of cases for this species. The results show a peak of contamination in scallops in 2012 followed by a steady decrease. Since 2014, levels of ASP toxins appear to be improving in this marine sub-region, with the number of exceedances of the regulatory limit below 1%.
Lead concentrations do not exceed the regulatory limit in any of the species sampled. The parameter is therefore considered to be met for lead.
The contamination of lipophilic toxins is lower than that of ASP toxins, but remains regular, with an average 2% exceedance over the 2010-2015 period. It should be noted that only dinophysistoxins exceed the regulatory limit. The percentage of exceedances is higher than the threshold, set at 0% in the framework of this assessment. The parameter is therefore not reached for lipophilic toxins.
Mercury concentrations show exceedances in one sample from the most consumed fish group (out of a total of 107 samples) and two samples from the predatory fish group (out of a total of 49 samples). Mercury levels in the other three groups (molluscs, cephalopods and crustaceans) remain below the regulatory limit. The percentage of exceedances is low overall but remains above the threshold set at 0% for this assessment. The parameter is therefore not reached for mercury.
The concentrations in ∑6PCB-NDL show some exceedances of the regulatory limit, for 3 samples from the most consumed fish group and 5 samples from the bivalve mollusc group. The percentage of exceedances is low overall but remains above the threshold, set at 0 % for this assessment. The parameter is therefore not reached for ∑6PCB-NDL.
The PSP toxin measurements show no exceedance of the regulatory limit in any of the bivalve molluscs sampled.
The percentage of exceedance of the sum of PAHs is relatively high, with more than 5% of samples above the maximum regulatory limit. The percentage of exceedances is above the threshold, set at 0% in this assessment. The parameter is therefore not reached for the sum of the 4 PAHs. In the period 2010-2015, these exceedances are only observed in 2015. It should be noted that there is a doubt as to the quality of the 2015 data for PAHs. In this context, it will be necessary to check whether this trend is confirmed in the following years.
PCDD/F concentrations do not exceed the regulatory limit in any of the species sampled. The parameter is therefore considered to be met for PCDD/F.
Related indicator
Criteria status
Not good
Not good
Not good
Not good
Good
Not good
Not good
Not good
Good
Not good
Good
Description criteria
Criterion D9C1 is in poor condition for benzo(a)pyrene because the parameter 'Concentration in biota' is not met for this substance. Indeed, exceedances of the regulatory limit (2 % of the samples) are observed for benzo(a)pyrene.
Criterion D9C1 is in poor condition for cadmium because the parameter "Concentration in biota" is not met for this substance. Indeed, exceedances of the regulatory limit (less than 1 % of the samples) are found for cadmium.
Criterion D9C1 is in poor condition for the sum of (PCDD/F + PCB-DL) because the parameter 'Concentration in biota' is not met for this group of contaminants. Indeed, exceedances of the regulatory limit (1 % of the samples) are found for the sum of (PCDD/F + PCB-DL).
Criterion D9C1 is in poor condition for ASP toxins because the parameter "Concentration in biota" is not met for these substances. Indeed, exceedances of the regulatory limit (12% of samples) are found for ASP toxins.
Criterion D9C1 is in good condition for lead because the parameter "Concentration in biota" is met for this substance. Indeed, no exceedance of the regulatory limit for lead is observed.
Criterion D9C1 is in poor condition for lipophilic toxins because the parameter "Concentration in biota" is not met for these substances. Indeed, exceedances of the regulatory limit (2% of samples) are observed for lipophilic toxins.
Criterion D9C1 is in poor condition for mercury because the parameter 'Concentration in biota' is not met for this substance. Indeed, exceedances of the regulatory limit (less than 1 % of the samples) are observed for mercury.
Criterion D9C1 is in poor condition for the 6 PCB-NDLs because the parameter "Concentration in biota" is not met for this group of contaminants. Indeed, exceedances of the regulatory limit (1 % of the samples) are found for all 6 PCB-NDLs.
Criterion D9C1 is in good condition for PSP toxins as the parameter 'Concentration in biota' is met for these substances. Indeed, no exceedance of the regulatory limit for PSP toxins is observed.
Criterion D9C1 is in poor condition for the sum of the 4 PAHs because the parameter 'Concentration in biota' is not met for this group of contaminants. Indeed, significant exceedances of the regulatory limit (5% of the samples) are observed for the sum of the 4 PAHs. It should be noted that these exceedances are mainly observed in 2015 and that there is a doubt as to the quality of the 2015 data for PAHs. In this context, it will be necessary to check whether this trend is confirmed in subsequent years.
Criterion D9C1 is in good condition for the sum of PCDD/F because the parameter 'Concentration in biota' is met for this group of contaminants. Indeed, no exceedance of the regulatory limit for the sum of PCDD/F is observed.
Element status
Not good
Not good
Not good
Not good
Good
Not good
Not good
Not good
Good
Not good
Good
Description element
The state of criterion D9C1 for benzo(a)pyrene provides direct information on the state of the element. The results for benzo(a)pyrene show an overall low percentage exceedance in the biota of concern (< 2%), but above the threshold. Benzo(a)pyrene is therefore considered to be in poor condition. It should be noted that the code of the additional element is a national code as no official reference system exists. The code "PRODPECH" refers to fishery products intended for human consumption and therefore includes multiple species (the most consumed fish, predatory fish, bivalve molluscs, crustaceans, cephalopods).
The status of criterion D9C1 for cadmium provides direct information on the status of the element. The cadmium results show an overall low percentage exceedance in the biota considered (< 1 %), but above the threshold. It should be noted that the code for the additional element is a national code as no official reference system exists. The code "PRODPECH" refers to fishery products intended for human consumption and therefore includes multiple species (the most consumed fish, predatory fish, bivalve molluscs, crustaceans, cephalopods).
The status of criterion D9C1 for dioxins and dioxin-like compounds provides direct information on the status of the element. The results for dioxins and dioxin-like compounds show an overall low percentage exceedence in the biota considered (< 2 %), but above the threshold. Dioxins and dioxin-like compounds are therefore considered to be in a poor state. It should be noted that the code for the additional element is a national code as no official reference exists. The code "PRODPECH" refers to fishery products intended for human consumption and therefore includes multiple species (most consumed fish, predatory fish, bivalve molluscs, crustaceans, cephalopods).
In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. The percentage of exceedance of SPA toxins is relatively high with more than 12% of samples above the regulatory maximum limit. Therefore, the PHA toxins are considered to be in poor condition. Note that the code of the element is taken from the Service d'administration nationale des données et référentiels sur l'eau (SANDRE: http://www.sandre.eaufrance.fr). Moreover, the code of the additional element is a national code as no official reference system exists. For example, the code "BIV" refers to bivalve molluscs and therefore includes several species (oysters, mussels and scallops).
No exceedances of the regulatory limit are observed for lead. Lead is therefore considered to be in good condition. It should be noted that the code for the additional element is a national code as no official reference exists. The code "PRODPECH" refers to fishery products intended for human consumption and therefore includes multiple species (the most consumed fish, predatory fish, bivalve molluscs, crustaceans, cephalopods).
In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to consider also algal toxins (phycotoxins) in the evaluation of criterion D9C1. Contamination of lipophilic toxins is lower than that of SPA, but remains regular, with an average of 2% exceedance over the period 2010-2015. Lipophilic toxins are therefore considered to be in poor condition.note that the code for the element "TOLI" is a national code due to the lack of an official reference. It refers to lipophilic toxins, namely okadaic acid, dinophysistoxins, pectenotoxins, azaspiracids, and yessotoxins. In addition, the additional element code is also a national code as no official reference exists. Thus, the "BIV" code refers to bivalve molluscs and therefore includes several species (oysters, mussels and scallops).
The status of criterion D9C1 for mercury directly informs the status of the element. The results for mercury show an overall low percentage exceedance in the biota considered (< 1%), but above the threshold. Note that the code for the additional element is a national code as no official reference system exists. The "PRODPECH" code refers to fishery products intended for human consumption and therefore includes multiple species (the most consumed fish, predatory fish, bivalve molluscs, crustaceans, cephalopods).
The status of criterion D9C1 for PCB-NDL directly informs the status of the element. The PCB-NDL results show an overall low percentage exceedance in the biota of concern (< 2 %), but above the threshold. Note that the additional element code is a national code as no official reference system exists. The code "PRODPECH" refers to fishery products intended for human consumption and therefore includes multiple species (the most consumed fish, predatory fish, bivalve molluscs, crustaceans, cephalopods).
In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to consider also algal toxins (phycotoxins) in the evaluation of criterion D9C1. No exceedance of the regulatory limit is observed for saxitoxins. Saxitoxins are therefore considered to be in good condition.note that the code of the element is from the "Service d'administration nationale des données et référentiels sur l'eau" (SANDRE: http://www.sandre.eaufrance.fr). In addition, the code of the additional element is a national code because no official reference system exists. Thus, the "BIV" code refers to bivalve molluscs and therefore includes several species (oysters, mussels and scallops).
The status of criterion D9C1 for the sum of the 4 ETAs directly informs the status of the element. The percentage of PAHs exceeded is relatively high, with more than 5% of samples exceeding the maximum regulatory limit. The sum of the 4 PAHs is therefore considered to be in poor condition. However, over the period 2010-2015, these exceedances are only observed in 2015 and there is doubt as to the quality of the 2015 data for PAHs. In this context, it will be necessary to check whether this trend is confirmed in the following years.note that the code of the additional element is a national code as no official reference exists. The "PRODPECH" code refers to fishery products intended for human consumption and therefore includes multiple species (the most consumed fish, predatory fish, bivalve molluscs, crustaceans, cephalopods).
No exceedance of the regulatory limit is observed for the sum of dioxins and furans. The sum of dioxins and furans is therefore considered to be in good condition. Note that the code for the additional element is a national code as no official reference exists. The code "PRODPECH" refers to fishery products intended for human consumption and therefore includes multiple species (the most consumed fish, predatory fish, bivalve molluscs, crustaceans, cephalopods).
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
Integration rule description parameter
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
No integration rule is necessary since only one parameter is evaluated to fill a criterion.
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
Integration rule description criteria
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
No integration rule is necessary, the criterion status directly informs the element status.
GES extent threshold
GES extent achieved
27.00
27.00
27.00
27.00
27.00
27.00
27.00
27.00
27.00
27.00
27.00
GES extent unit
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
GES achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description overall status
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
The results obtained at the scale of the Channel - North Sea marine sub-region show that 8 contaminants, or groups of contaminants, are not in good condition out of the 11 considered. In the framework of Decision 2017/848/EU, only chemical contaminants were retained for the evaluation of descriptor 9. However, at the national level, France proposes to also consider algal toxins (phycotoxins) in the evaluation of criterion D9C1. Thus, the 11 contaminants, or groups of contaminants, considered for this evaluation include 8 groups of chemical contaminants and 3 groups of phycotoxins. In addition, this assessment is based on extensive analytical data from bivalve molluscs. Because of their filtering role, these species are a good indicator of the ecological status of the surrounding environment and therefore allow the ecological status of coastal areas to be assessed. The use of fish data can, in turn, provide an assessment of the ecological status of the offshore. However, these data are patchy and additional efforts are required, in terms of the exact source and number of samples considered, particularly at the upper links of the food web. The threshold at parameter level, set at 0% exceedance of regulatory maximum limits, results in a poor state of the contaminant, or group of contaminants, for a single exceedance over several tens or even hundreds of measurements. This threshold therefore lacks robustness within the framework of a long-term management policy. The setting of a tolerance threshold will therefore have to be discussed at European level between the different Member States.
Assessments period
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
Related pressures
Related targets