Member State report / Art11 / 2020 / D9 / Poland / Baltic Sea
Report type | Member State report to Commission |
MSFD Article | Art. 11 Monitoring programmes (and Art. 17 updates) |
Report due | 2020-10-15 |
GES Descriptor | D9 Contaminants in seafood |
Member State | Poland |
Region/subregion | Baltic Sea |
Reported by | Chief Inspectorate of Environmental Protection |
Report date | 2021-12-31 |
Report access |
Descriptor |
D9 |
D9 |
D9 |
D9 |
D9 |
D9 |
D9 |
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Monitoring strategy description |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which contaminants in fish and other seafood for human consumption do not exceed levels established by Union legislation or other relevant standards. The strategy concerns the monitoring of the level of hazardous substances in fish exploited commercially. The strategy includes research in the range of concentrations of selected substances in samples collected systematically at selected stations and locations with the assumed frequency. The choice of substances to be monitored results from the current legislation and the analysis of current pressures. Both the network of stations / locations and the frequency are adjusted to the specificity of the substances of concern - indicators. The strategy takes into account regional arrangements (cooperation within HELCOM), both in terms of the assessed indicators, as well as spatial and temporal resolution guaranteeing the obtaining of results that can be the basis for holistic assessment in the entire Baltic Sea area. The strategy concerns monitoring investigations, which are primarily to provide information on the current status of the marine environment. The assessment of the status of the environment in terms of the indicators is carried out by relating the current concentrations of the hazardous substance to the threshold values set at European, regional or national level. The information obtained is the basis for tracking changes taking place in the environment, mainly as a result of the measures taken, which are determined on the basis of the analysis of the current situation, properties typical for good environmental status and environmental targets. |
Coverage of GES criteria |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Gaps and plans |
There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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There are not gaps identified.
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Related targets |
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Coverage of targets |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Related measures |
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Coverage of measures |
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Related monitoring programmes |
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Programme code |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
PL-D08-01 |
Programme name |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Contaminant levels - in species, including seafood |
Update type |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
Old programme codes |
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Programme description |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme of contaminant levels in organisms, including commercially exploited species, covers research on fish collected once a year during the summer season from 7 locations: Władysławowo fishery, Kolobrzeg – Darłowo fishery, Gdańsk Basin, Pomeranian Bay, Szczecin Lagoon, Vistula lagoon and Central Coast, studies of mussels collected once a year during summer at one location in the Sopot area and studies of macrophytes collected from 4 locations: Orłowski Cliff, Jama Kuźnicka, Słupsk Bank, Rowy. In fish muscle tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, organochlorine pesticides, mercury, arsenic and 137Cs are analysed. In fish liver lead, cadmium, zinc i copper are analysed. In fish bile polyaromatic hydrocarbon metabolites are analysed. In mussel soft tissue polybrominated diphenyl ethers, hexabromocyclododecane, perfluorooctane sulphonate, perfluorooctanoic acid, polychlorinated biphenyls, organotin compounds, polyaromatic hydrocarbons, organochlorine pesticides, lead, cadmium, mercury, arsenic, zinc and copper are analysed. In macrophyte tissue lead, cadmium, mercury, arsenic, zinc, copper 137Cs are analysed. The programme also covers analysis of arsenic in fish as a possible indicator of pollution with chemical warfare agents. Arsenic is analysed in fish muscle tissue collected from 4 locations of the deep sea area.
Data on dioxins, furans and dioxin-like polychlorinated biphenyls are collected within dioxin monitoring conducted under National Control Programme of dioxins (PCDD), furans (PCDF), dioxin-like polychlorinated biphenyls (dl-PCB) and non-dioxin-like PCBs (ndl-PCB) in animal food products supervised by General Veterinary Inspectorate. Monitoring assumes the assimilation of data from WFD monitoring. |
Monitoring purpose |
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Other policies and conventions |
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Regional cooperation - coordinating body |
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Regional cooperation - countries involved |
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Regional cooperation - implementation level |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Monitoring details |
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Features |
Contaminants - non UPBT substances
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Contaminants - non UPBT substances
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Contaminants - non UPBT substances
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Contaminants - non UPBT substances
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Contaminants - non UPBT substances
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Contaminants - non UPBT substances
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Contaminants - UPBT substances
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Contaminants - UPBT substances
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Contaminants - UPBT substances
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Contaminants - UPBT substances
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Contaminants – in seafood
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Contaminants – in seafood
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Contaminants – in seafood
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Contaminants – in seafood
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Elements |
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GES criteria |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D9C1 |
D9C1 |
D9C1 |
D9C1 |
Parameters |
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Parameter Other |
Macrophytes |
Macrophytes |
Macrophytes |
Macrophytes |
Macrophytes |
Macrophytes |
Fish muscle: herring, perch and flounder |
Fish liver: herring, perch and flounder |
Fish muscle: herring, perch and flounder |
Fish liver: herring, perch and flounder |
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Spatial scope |
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Marine reporting units |
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Temporal scope (start date - end date) |
1998 |
1998 |
1998 |
1998 |
1998 |
1998 |
1998 |
1998 |
1998 |
1998 |
1998 |
1998 |
1998 |
1998 |
Monitoring frequency |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Monitoring type |
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Monitoring method |
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Monitoring method other |
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Quality control |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
According to HELCOM recommendations and internal procedures, including the application of the requirements of the standard: ISO / IEC 17025 General requirements for the competence of testing and calibration laboratories |
Data management |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Raw and processed data are stored in a dedicated database of the Chief Inspectorate of Environmental Protection |
Data access |
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Related indicator/name |
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Contact |
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References |