Member State report / Art11 / 2020 / D8 / 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 | D8 Contaminants |
| Member State | Poland |
| Region/subregion | Baltic Sea |
| Reported by | Chief Inspectorate of Environmental Protection |
| Report date | 2021-12-31 |
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Monitoring strategy description |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
The goal of the Strategy is to achieve the status of the marine environment in which concentrations of contaminants are at levels not giving rise to pollution effects.The strategy concerns the monitoring of the level of hazardous substances in various matrices: biota, sediments, seawater and the effects of their impact on marine organisms. 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, regional arrangements (HELCOM) 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 in selected matrixes - 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 of good environmental status (permissible concentrations of hazardous substances, below which there are no harmful effects) and environmental targets. |
Coverage of GES criteria |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Gaps and plans |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Extending the scope of research on biological effects with new indicators |
Related targets |
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Coverage of targets |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Related measures |
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Coverage of measures |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
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 |
PL-D08-02 |
PL-D08-02 |
PL-D08-02 |
PL-D08-02 |
PL-D08-03 |
PL-D08-03 |
PL-D08-03 |
PL-D08-03 |
PL-D08-04 |
PL-D08-04 |
PL-D08-05 |
PL-D08-05 |
PL-D08-05 |
PL-D08-05 |
PL-D1.1-03 |
PL-D1.1-03 |
PL-D1.1-03 |
PL-D1.1-03 |
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 |
Contaminant levels - in sediment |
Contaminant levels - in sediment |
Contaminant levels - in sediment |
Contaminant levels - in sediment |
Contaminant levels - in water |
Contaminant levels - in water |
Contaminant levels - in water |
Contaminant levels - in water |
Contaminant inputs – acute pollution events, incl. oil spills |
Contaminant inputs – acute pollution events, incl. oil spills |
Mobile species – fish – health status |
Mobile species – fish – health status |
Mobile species – fish – health status |
Mobile species – fish – health status |
Mobile species - birds - health status |
Mobile species - birds - health status |
Mobile species - birds - health status |
Mobile species - birds - health status |
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 |
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 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
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. |
The programme of contaminant levels in sediment includes analyses of organochlorine pesticides, polychlorinated biphenyls. polyaromatic hydrocarbons, cadmium, lead, mercury, aluminium, arsenic, copper, zinc, organotin compounds and sulfur mustard in stratified sediments collected once every 6 years in four locations: Gdańsk Deep, Bornholm Deep, south-eastern Gotland Basin, Bornholm Basin, sampled once every 3 years in 2 locations: Vistula lagoon and Szczecin lagoon.
The programme also includes measurements and analysis of arsenic and sulfur mustard as indicators of potential contamination with chemical warfare agents and PAHs as indicators of contamination with petroleum products, the source of which is fuel from shipwrecks. Arsenic and sulfur mustard are analysed in sediment samples from six locations from the open sea and the Gulf of Gdańsk. PAH monitoring includes analysis of sediment samples from five locations from the Puck Bay and the Gulf of Gdańsk. Samples are collected once a year. |
The programme of contaminant levels in sediment includes analyses of organochlorine pesticides, polychlorinated biphenyls. polyaromatic hydrocarbons, cadmium, lead, mercury, aluminium, arsenic, copper, zinc, organotin compounds and sulfur mustard in stratified sediments collected once every 6 years in four locations: Gdańsk Deep, Bornholm Deep, south-eastern Gotland Basin, Bornholm Basin, sampled once every 3 years in 2 locations: Vistula lagoon and Szczecin lagoon.
The programme also includes measurements and analysis of arsenic and sulfur mustard as indicators of potential contamination with chemical warfare agents and PAHs as indicators of contamination with petroleum products, the source of which is fuel from shipwrecks. Arsenic and sulfur mustard are analysed in sediment samples from six locations from the open sea and the Gulf of Gdańsk. PAH monitoring includes analysis of sediment samples from five locations from the Puck Bay and the Gulf of Gdańsk. Samples are collected once a year. |
The programme of contaminant levels in sediment includes analyses of organochlorine pesticides, polychlorinated biphenyls. polyaromatic hydrocarbons, cadmium, lead, mercury, aluminium, arsenic, copper, zinc, organotin compounds and sulfur mustard in stratified sediments collected once every 6 years in four locations: Gdańsk Deep, Bornholm Deep, south-eastern Gotland Basin, Bornholm Basin, sampled once every 3 years in 2 locations: Vistula lagoon and Szczecin lagoon.
The programme also includes measurements and analysis of arsenic and sulfur mustard as indicators of potential contamination with chemical warfare agents and PAHs as indicators of contamination with petroleum products, the source of which is fuel from shipwrecks. Arsenic and sulfur mustard are analysed in sediment samples from six locations from the open sea and the Gulf of Gdańsk. PAH monitoring includes analysis of sediment samples from five locations from the Puck Bay and the Gulf of Gdańsk. Samples are collected once a year. |
The programme of contaminant levels in sediment includes analyses of organochlorine pesticides, polychlorinated biphenyls. polyaromatic hydrocarbons, cadmium, lead, mercury, aluminium, arsenic, copper, zinc, organotin compounds and sulfur mustard in stratified sediments collected once every 6 years in four locations: Gdańsk Deep, Bornholm Deep, south-eastern Gotland Basin, Bornholm Basin, sampled once every 3 years in 2 locations: Vistula lagoon and Szczecin lagoon.
The programme also includes measurements and analysis of arsenic and sulfur mustard as indicators of potential contamination with chemical warfare agents and PAHs as indicators of contamination with petroleum products, the source of which is fuel from shipwrecks. Arsenic and sulfur mustard are analysed in sediment samples from six locations from the open sea and the Gulf of Gdańsk. PAH monitoring includes analysis of sediment samples from five locations from the Puck Bay and the Gulf of Gdańsk. Samples are collected once a year. |
The programme contaminant levels in water includes analysis of 137Cs and 90Sr in seawater samples collected once a year at 17 monitoring stations from surface and near-bottom layers and every 20 m depths at 5 monitoring stations as well as analysis of pharmaceuticals: diclofenac and 17-alpha ethinylestradiol in surface water collected once a year at 9 monitoring stations. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme contaminant levels in water includes analysis of 137Cs and 90Sr in seawater samples collected once a year at 17 monitoring stations from surface and near-bottom layers and every 20 m depths at 5 monitoring stations as well as analysis of pharmaceuticals: diclofenac and 17-alpha ethinylestradiol in surface water collected once a year at 9 monitoring stations. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme contaminant levels in water includes analysis of 137Cs and 90Sr in seawater samples collected once a year at 17 monitoring stations from surface and near-bottom layers and every 20 m depths at 5 monitoring stations as well as analysis of pharmaceuticals: diclofenac and 17-alpha ethinylestradiol in surface water collected once a year at 9 monitoring stations. Monitoring assumes the assimilation of data from WFD monitoring. |
The programme contaminant levels in water includes analysis of 137Cs and 90Sr in seawater samples collected once a year at 17 monitoring stations from surface and near-bottom layers and every 20 m depths at 5 monitoring stations as well as analysis of pharmaceuticals: diclofenac and 17-alpha ethinylestradiol in surface water collected once a year at 9 monitoring stations. Monitoring assumes the assimilation of data from WFD monitoring. |
The parameter characterizing oil spills is the average annual spill volume expressed in m3 in a specific assessment area. Data for this parameter are obtained from aerial observations supervised by the Maritime Office in Gdynia. The data are obtained from HELCOM assessments of the HELCOM Core Indicator: Operational oil spills from ship (https://helcom.fi/baltic-sea-trends/indicators/). |
The parameter characterizing oil spills is the average annual spill volume expressed in m3 in a specific assessment area. Data for this parameter are obtained from aerial observations supervised by the Maritime Office in Gdynia. The data are obtained from HELCOM assessments of the HELCOM Core Indicator: Operational oil spills from ship (https://helcom.fi/baltic-sea-trends/indicators/). |
Two parameters are monitored within the monitoring programme of mobile species – fish – health status: micronucleus test - genotoxicity index (monitored since 2014) end externally visible fish diseases (monitored since 1994).
In order to perform the micronucleus test, fish blood samples are collected once a year in 4 to 6 assessment areas. The analysis of aberrations with micronucleus test method is performed by means of microscopy analysis.
The monitoring of externally visible fish diseases is performed on all fish species collected within monitoring of deep-sea, shallow areas of the open sea and transitional and coastal waters.
MIR-PIB began observations of external pathological changes in Baltic fish in 1980 and from 1994 this institute performs systematic monitoring in this field. The methodology applied in monitoring programme performed by MIR-PIB has been developed based on recommendations of the International Council for the Exploration of the Sea (ICES), that coordinates research on the international scale. National reports on the occurrence of externally visible fish diseases are drawn annually and presented at meetings of ICES Working Group on Pathology and Diseases of Marine Organisms (WGPDMO). Research conducted by MIR-PIB cover recording of only 3 diseases (skin ulcers, lymphocytosis and skeletal deformities).
In 2021 additional pilot monitoring of pathological changes has been conducted for 2 fish species – cod Gadus morhua and flounder Platichthys flesus – neceserry to calculate fish disease index – FDI (6-9 pathological changes depending on the species). Selected individuals will be submitted to standard ichthyological analysis. The mass of gonads and liver of monitored fish will also be determined. The analysis of pathological changes will focus on subsequent diseases:
flatfish – lymphocystis, ulceration, fin diseases, skeletal deformities, existance of parasites (Lepeophtheirus pectoralis i Cryptocotyle sp.), macroscopic liver neoplasms, non-specific histopathological liver lesions, histopathological contaminant specific liver lesions;
cod – ulcers, epidermal hyperplasia/papilloma, fin disease, skeletal deformities, gill disease, existance of parasites (Lepeophtheirus pectoralis and Cryptocotyle sp.), macroscopic liver neoplasms, non-specific histopathological liver lesions, histopathological contaminant specific liver lesions.
The research will be performed in 2 waterbodies (Outher Puck Bay and Inner Gulf of Gdańsk) in order to extens |
Two parameters are monitored within the monitoring programme of mobile species – fish – health status: micronucleus test - genotoxicity index (monitored since 2014) end externally visible fish diseases (monitored since 1994).
In order to perform the micronucleus test, fish blood samples are collected once a year in 4 to 6 assessment areas. The analysis of aberrations with micronucleus test method is performed by means of microscopy analysis.
The monitoring of externally visible fish diseases is performed on all fish species collected within monitoring of deep-sea, shallow areas of the open sea and transitional and coastal waters.
MIR-PIB began observations of external pathological changes in Baltic fish in 1980 and from 1994 this institute performs systematic monitoring in this field. The methodology applied in monitoring programme performed by MIR-PIB has been developed based on recommendations of the International Council for the Exploration of the Sea (ICES), that coordinates research on the international scale. National reports on the occurrence of externally visible fish diseases are drawn annually and presented at meetings of ICES Working Group on Pathology and Diseases of Marine Organisms (WGPDMO). Research conducted by MIR-PIB cover recording of only 3 diseases (skin ulcers, lymphocytosis and skeletal deformities).
In 2021 additional pilot monitoring of pathological changes has been conducted for 2 fish species – cod Gadus morhua and flounder Platichthys flesus – neceserry to calculate fish disease index – FDI (6-9 pathological changes depending on the species). Selected individuals will be submitted to standard ichthyological analysis. The mass of gonads and liver of monitored fish will also be determined. The analysis of pathological changes will focus on subsequent diseases:
flatfish – lymphocystis, ulceration, fin diseases, skeletal deformities, existance of parasites (Lepeophtheirus pectoralis i Cryptocotyle sp.), macroscopic liver neoplasms, non-specific histopathological liver lesions, histopathological contaminant specific liver lesions;
cod – ulcers, epidermal hyperplasia/papilloma, fin disease, skeletal deformities, gill disease, existance of parasites (Lepeophtheirus pectoralis and Cryptocotyle sp.), macroscopic liver neoplasms, non-specific histopathological liver lesions, histopathological contaminant specific liver lesions.
The research will be performed in 2 waterbodies (Outher Puck Bay and Inner Gulf of Gdańsk) in order to extens |
Two parameters are monitored within the monitoring programme of mobile species – fish – health status: micronucleus test - genotoxicity index (monitored since 2014) end externally visible fish diseases (monitored since 1994).
In order to perform the micronucleus test, fish blood samples are collected once a year in 4 to 6 assessment areas. The analysis of aberrations with micronucleus test method is performed by means of microscopy analysis.
The monitoring of externally visible fish diseases is performed on all fish species collected within monitoring of deep-sea, shallow areas of the open sea and transitional and coastal waters.
MIR-PIB began observations of external pathological changes in Baltic fish in 1980 and from 1994 this institute performs systematic monitoring in this field. The methodology applied in monitoring programme performed by MIR-PIB has been developed based on recommendations of the International Council for the Exploration of the Sea (ICES), that coordinates research on the international scale. National reports on the occurrence of externally visible fish diseases are drawn annually and presented at meetings of ICES Working Group on Pathology and Diseases of Marine Organisms (WGPDMO). Research conducted by MIR-PIB cover recording of only 3 diseases (skin ulcers, lymphocytosis and skeletal deformities).
In 2021 additional pilot monitoring of pathological changes will be conducted for 2 fish species – cod Gadus morhua and flounder Platichthys flesus – neceserry to calculate fish disease index – FDI (6-9 pathological changes depending on the species). Selected individuals will be submitted to standard ichthyological analysis. The mass of gonads and liver of monitored fish will also be determined. The analysis of pathological changes will focus on subsequent diseases:
flatfish – lymphocystis, ulceration, fin diseases, skeletal deformities, existance of parasites (Lepeophtheirus pectoralis i Cryptocotyle sp.), macroscopic liver neoplasms, non-specific histopathological liver lesions, histopathological contaminant specific liver lesions;
cod – ulcers, epidermal hyperplasia/papilloma, fin disease, skeletal deformities, gill disease, existance of parasites (Lepeophtheirus pectoralis and Cryptocotyle sp.), macroscopic liver neoplasms, non-specific histopathological liver lesions, histopathological contaminant specific liver lesions.
The research will be performed in 2 waterbodies (Outher Puck Bay and Inner Gulf of Gdańsk) in order to extensi |
Two parameters are monitored within the monitoring programme of mobile species – fish – health status: micronucleus test - genotoxicity index (monitored since 2014) end externally visible fish diseases (monitored since 1994).
In order to perform the micronucleus test, fish blood samples are collected once a year in 4 to 6 assessment areas. The analysis of aberrations with micronucleus test method is performed by means of microscopy analysis.
The monitoring of externally visible fish diseases is performed on all fish species collected within monitoring of deep-sea, shallow areas of the open sea and transitional and coastal waters.
MIR-PIB began observations of external pathological changes in Baltic fish in 1980 and from 1994 this institute performs systematic monitoring in this field. The methodology applied in monitoring programme performed by MIR-PIB has been developed based on recommendations of the International Council for the Exploration of the Sea (ICES), that coordinates research on the international scale. National reports on the occurrence of externally visible fish diseases are drawn annually and presented at meetings of ICES Working Group on Pathology and Diseases of Marine Organisms (WGPDMO). Research conducted by MIR-PIB cover recording of only 3 diseases (skin ulcers, lymphocytosis and skeletal deformities).
In 2021 additional pilot monitoring of pathological changes will be conducted for 2 fish species – cod Gadus morhua and flounder Platichthys flesus – neceserry to calculate fish disease index – FDI (6-9 pathological changes depending on the species). Selected individuals will be submitted to standard ichthyological analysis. The mass of gonads and liver of monitored fish will also be determined. The analysis of pathological changes will focus on subsequent diseases:
flatfish – lymphocystis, ulceration, fin diseases, skeletal deformities, existance of parasites (Lepeophtheirus pectoralis i Cryptocotyle sp.), macroscopic liver neoplasms, non-specific histopathological liver lesions, histopathological contaminant specific liver lesions;
cod – ulcers, epidermal hyperplasia/papilloma, fin disease, skeletal deformities, gill disease, existance of parasites (Lepeophtheirus pectoralis and Cryptocotyle sp.), macroscopic liver neoplasms, non-specific histopathological liver lesions, histopathological contaminant specific liver lesions.
The research will be performed in 2 waterbodies (Outher Puck Bay and Inner Gulf of Gdańsk) in order to extensi |
White-tailed Eagle Productivity Monitoring is carried out to meet the requirements of the Birds Directive as well as the Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017 for Descriptors D1 and D8. The results of the monitoring are also used for the work of the HELCOM group |
White-tailed Eagle Productivity Monitoring is carried out to meet the requirements of the Birds Directive as well as the Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017 for Descriptors D1 and D8. The results of the monitoring are also used for the work of the HELCOM group |
White-tailed Eagle Productivity Monitoring is carried out to meet the requirements of the Birds Directive as well as the Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017 for Descriptors D1 and D8. The results of the monitoring are also used for the work of the HELCOM group |
White-tailed Eagle Productivity Monitoring is carried out to meet the requirements of the Birds Directive as well as the Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017 for Descriptors D1 and D8. The results of the monitoring are also used for the work of the HELCOM group |
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 |
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 |
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Monitoring details |
All known nests sites in the coastal zone (up to 10km from the coast) are inspected in every breeding season from the ground (early spring) and by climbing the nest tree (active nests in late spring). The monitoring includes the control of 107 known breeding sites of White-tailed Eagle on the Polish Baltic coast in a 10 km wide strip from the shoreline. The main goal of the study is to determine the reproductive parameters of the coastal population of the species.
White-tailed eagle's productivity is described by three indicators:
1) mean number of chicks per pair entering reproduction;
2) mean number of chicks per pair with successful breeding;
3) breeding success - an indicator defining the percentage share of pairs that brood chicks in relation to the number of all pairs with known final hatching effect. |
All known nests sites in the coastal zone (up to 10km from the coast) are inspected in every breeding season from the ground (early spring) and by climbing the nest tree (active nests in late spring). The monitoring includes the control of 107 known breeding sites of White-tailed Eagle on the Polish Baltic coast in a 10 km wide strip from the shoreline. The main goal of the study is to determine the reproductive parameters of the coastal population of the species.
White-tailed eagle's productivity is described by three indicators:
1) mean number of chicks per pair entering reproduction;
2) mean number of chicks per pair with successful breeding;
3) breeding success - an indicator defining the percentage share of pairs that brood chicks in relation to the number of all pairs with known final hatching effect. |
All known nests sites in the coastal zone (up to 10km from the coast) are inspected in every breeding season from the ground (early spring) and by climbing the nest tree (active nests in late spring). The monitoring includes the control of 107 known breeding sites of White-tailed Eagle on the Polish Baltic coast in a 10 km wide strip from the shoreline. The main goal of the study is to determine the reproductive parameters of the coastal population of the species.
White-tailed eagle's productivity is described by three indicators:
1) mean number of chicks per pair entering reproduction;
2) mean number of chicks per pair with successful breeding;
3) breeding success - an indicator defining the percentage share of pairs that brood chicks in relation to the number of all pairs with known final hatching effect. |
All known nests sites in the coastal zone (up to 10km from the coast) are inspected in every breeding season from the ground (early spring) and by climbing the nest tree (active nests in late spring). The monitoring includes the control of 107 known breeding sites of White-tailed Eagle on the Polish Baltic coast in a 10 km wide strip from the shoreline. The main goal of the study is to determine the reproductive parameters of the coastal population of the species.
White-tailed eagle's productivity is described by three indicators:
1) mean number of chicks per pair entering reproduction;
2) mean number of chicks per pair with successful breeding;
3) breeding success - an indicator defining the percentage share of pairs that brood chicks in relation to the number of all pairs with known final hatching effect. |
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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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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 - 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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Acute pollution events
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Acute pollution events
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Adverse effects on species or habitats
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Adverse effects on species or habitats
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Adverse effects on species or habitats
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Adverse effects on species or habitats
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Surface-feeding birds
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Surface-feeding birds
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Surface-feeding birds
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Adverse effects on species or habitats
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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 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
D1C2 |
D1C3 |
D1C4 |
D8C2 |
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 |
Not relevant |
Not relevant |
micronucleus test - genotoxicity index |
Externally visible fish diseases |
micronucleus test - genotoxicity index |
Externally visible fish diseases |
White-tailed Eagle Breedning Productivity |
Productivity |
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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 |
1998 |
1998 |
1998 |
1998 |
1985 |
1985 |
1985 |
1985 |
2011 |
2011 |
1980-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
Monitoring frequency |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
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 |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl Podręcznik do monitoringu elementów biologicznych i klasyfikacji stanu ekologicznego wód powierzchniowych. Aktualizacja metod. (GIOŚ 2020) https://www.gios.gov.pl/images/dokumenty/pms/monitoring_wod/Podrecznik_Monitoringu_Wod.pdf |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl Podręcznik do monitoringu elementów biologicznych i klasyfikacji stanu ekologicznego wód powierzchniowych. Aktualizacja metod. (GIOŚ 2020) https://www.gios.gov.pl/images/dokumenty/pms/monitoring_wod/Podrecznik_Monitoringu_Wod.pdf |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
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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 |
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
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According to HELCOM recommendations
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According to HELCOM recommendations. Screening programme ICES DATRAS centre. |
According to HELCOM recommendations. Screening programme ICES DATRAS centre. |
According to HELCOM recommendations. Screening programme ICES DATRAS centre. |
According to HELCOM recommendations. Screening programme ICES DATRAS centre. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
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 |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
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Data access |
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Related indicator/name |
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Contact |
Person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
National coordinator of monitoring programme: Zdzisław Cenian cenian@wp.pl |
Person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
National coordinator of monitoring programme: Zdzisław Cenian cenian@wp.pl |
Person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
National coordinator of monitoring programme: Zdzisław Cenian cenian@wp.pl |
Person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
National coordinator of monitoring programme: Zdzisław Cenian cenian@wp.pl |
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References |