Member State report / Art11 / 2020 / D5 / 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 D5 Eutrophication
Member State Poland
Region/subregion Baltic Sea
Reported by Chief Inspectorate of Environmental Protection
Report date 2021-12-31
Report access

Descriptor
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Monitoring strategy description
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to provide information for the assessments of the status of marine waters with regard to eutrophication and its effects. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. Monitoring of eutrophication and its effects will enable to identify measures to be implemented and progress of those already implemented to achieve good environmental status of marine waters, in accordance with the initial assessment of the status of marine waters and the set of characteristics for the good environmental status of marine waters, provide information to assess the impact of the measures set out in the programme of measures, enable identification of the cause of changes in the environmental status of marine waters and undertake possible corrective measures to restore the good environmental status of marine waters. The Strategy incorporates information gathered within 4 monitoring programmes: water column chemical and physical characteristics and benthic communities and species characteristics.Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
Coverage of GES criteria
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Gaps and plans
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Related targets
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
  • PL_Target_D5
  • PL_Target_D5C1
  • PL_Target_D5C2
  • PL_Target_D5C3
  • PL_Target_D5C4
  • PL_Target_D5C5
  • PL_Target_D5C6
  • PL_Target_D5C7
  • PL_Target_D5C8
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
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
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
  • BALPL-M018 - 'KTM4_1 Reducing emissions of phosphorus from the heap of phosphogypsum in Wiślinka'
  • BALPL-M019 - 'KTM1_1 Increasing requirements for phosphorus removal in wastewater discharged from wastewater treatment plants'
  • BALPL-M020 - 'KTM2_2 Increasing the amount of land covered by fertilization plans'
  • BALPL-M025 - 'KTM2_5 The use of irrigation channels to reduce the load of nutrients from agricultural land'
  • BALPL-M027 - 'KTM1_2 Evaluation of technical and economic feasibility of increasing the nitrogen reduction at selected wastewater treatment plants of the chemical industry'
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
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
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
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  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
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  • PL-D05-01
  • PL-D06-01
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  • PL-D05-01
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  • PL-D05-01
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  • PL-D06-02
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  • PL-D06-02
  • PL-D07-01
  • PL-D05-01
  • PL-D06-01
  • PL-D06-02
  • PL-D07-01
Programme code
PL-D05-01
PL-D05-01
PL-D05-01
PL-D05-01
PL-D05-01
PL-D05-01
PL-D05-01
PL-D05-01
PL-D05-01
PL-D05-01
PL-D06-01
PL-D06-01
PL-D06-01
PL-D06-01
PL-D06-01
PL-D06-01
PL-D06-01
PL-D06-01
PL-D06-02
PL-D06-02
PL-D06-02
PL-D06-02
PL-D06-02
PL-D06-02
PL-D06-02
PL-D06-02
PL-D06-02
PL-D06-02
PL-D07-01
PL-D07-01
PL-D07-01
PL-D07-01
PL-D07-01
PL-D07-01
PL-D07-01
PL-D07-01
Programme name
Water column - chemical characteristics
Water column - chemical characteristics
Water column - chemical characteristics
Water column - chemical characteristics
Water column - chemical characteristics
Water column - chemical characteristics
Water column - chemical characteristics
Water column - chemical characteristics
Water column - chemical characteristics
Water column - chemical characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Benthic species – abundance or biomass
Benthic species – abundance or biomass
Benthic species – abundance or biomass
Benthic species – abundance or biomass
Benthic species – abundance or biomass
Benthic species – abundance or biomass
Benthic species – abundance or biomass
Benthic species – abundance or biomass
Benthic species – abundance or biomass
Benthic species – abundance or biomass
Water column - physical characteristics
Water column - physical characteristics
Water column - physical characteristics
Water column - physical characteristics
Water column - physical characteristics
Water column - physical characteristics
Water column - physical characteristics
Water column - physical characteristics
Update type
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New programme
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New programme
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New programme
New programme
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New programme
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New programme
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New programme
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New programme
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New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
Old programme codes
Programme description
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
Monitoring of chemical parameters is carried out in the assessment units in accordance with the current HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 24 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 measurements per year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only).
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only).
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only).
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only).
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only).
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only).
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only).
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only).
Monitoring purpose
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
Other policies and conventions
Regional cooperation - coordinating body
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
Regional cooperation - countries involved
Regional cooperation - implementation level
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Monitoring details
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September).
The use of Ferry-Box data dependent on its availability. The use of satellite products, information dependent on data availability.
The use of Ferry-Box data dependent on its availability. The use of satellite products, information dependent on data availability.
The use of Ferry-Box data dependent on its availability. The use of satellite products, information dependent on data availability.
The use of Ferry-Box data dependent on its availability. The use of satellite products, information dependent on data availability.
The use of Ferry-Box data dependent on its availability. The use of satellite products, information dependent on data availability.
The use of Ferry-Box data dependent on its availability. The use of satellite products, information dependent on data availability.
The use of Ferry-Box data dependent on its availability. The use of satellite products, information dependent on data availability.
The use of Ferry-Box data dependent on its availability. The use of satellite products, information dependent on data availability.
Features
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Chemical characteristics
Chemical characteristics
Chemical characteristics
Chemical characteristics
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Benthic broad habitats
Benthic broad habitats
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Eutrophication
Eutrophication
Physical and hydrological characteristics
Physical and hydrological characteristics
Physical and hydrological characteristics
Physical and hydrological characteristics
Physical and hydrological characteristics
Physical and hydrological characteristics
Elements
  • DIN
  • DIP
  • TN
  • TP
  • DIN
  • DIP
  • TN
  • TP
  • Dissolved oxygen (O2)
  • Dissolved oxygen (O2)
  • Dissolved carbon dioxide (pCO2)
  • pH
  • Dissolved carbon dioxide (pCO2)
  • pH
  • Silicate (SiO4)
  • Silicate (SiO4)
  • Benthic habitats - opportunistic macroalgae
  • Benthic habitats - opportunistic macroalgae
  • Benthic habitats - macrophyte communities
  • Benthic habitats - macrophyte communities
  • Benthic habitats - macrobenthic communities
  • Benthic habitats - macrobenthic communities
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats - opportunistic macroalgae
  • Benthic habitats - opportunistic macroalgae
  • Benthic habitats - macrophyte communities
  • Benthic habitats - macrophyte communities
  • Benthic habitats - macrobenthic communities
  • Benthic habitats - macrobenthic communities
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Transparency
  • Transparency
  • Temperature
  • Transparency
  • Water density
  • Temperature
  • Transparency
  • Water density
GES criteria
D5C1
D5C1
D5C5
D5C5
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
D5C6
D5C6
D5C7
D5C7
D5C8
D5C8
D6C5
D6C5
D5C6
D5C6
D5C7
D5C7
D5C8
D5C8
D6C5
D6C5
NotRelevan
NotRelevan
D5C4
D5C4
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
Parameters
  • Concentration in water
  • Concentration in water
  • Concentration in water
  • Concentration in water
  • pco2 - alkalinity
  • Ph
  • pco2 - alkalinity
  • Ph
  • Concentration in water
  • Concentration in water
  • Coverage (e.g. of a species within a habitat or area)
  • Extent
  • Coverage (e.g. of a species within a habitat or area)
  • Extent
  • Coverage (e.g. of a species within a habitat or area)
  • Extent
  • Coverage (e.g. of a species within a habitat or area)
  • Extent
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Other
  • Other
  • Coverage (e.g. of a species within a habitat or area)
  • Extent
  • Coverage (e.g. of a species within a habitat or area)
  • Extent
  • Coverage (e.g. of a species within a habitat or area)
  • Extent
  • Coverage (e.g. of a species within a habitat or area)
  • Extent
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Other
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Species composition
  • Abundance (number of individuals)
  • Biomass
  • Species composition
  • Transparency of water
  • Transparency of water
  • Temperature
  • Transparency of water
  • Salinity
  • Temperature
  • Transparency of water
  • Salinity
Parameter Other
silicate
silicate
Species composition, abundance/coverage and biomas
Species composition, abundance/coverage and biomas
Species composition, abundance/coverage and biomas
Species composition, abundance/coverage and biomas
Spatial scope
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
Marine reporting units
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL
  • L2-SEA-009-POL
  • L4-POL-001
  • L4-POL-002
  • L4-POL-003
  • L4-POL-004
  • L4-POL-005
  • L4-POL-006
  • L4-POL-007
  • L4-POL-008
  • L4-POL-009
  • L4-POL-010
  • L4-POL-011
  • L4-POL-012
  • L4-POL-013
  • L4-POL-014
  • L4-POL-015
  • L4-POL-016
  • L4-POL-017
  • L4-POL-018
  • L4-POL-019
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
  • L2-SEA-007-POL
  • L2-SEA-008-POL_1
  • L2-SEA-009-POL
  • L4-POL-020
  • L4-POL-021
  • L4-POL-022
  • L4-POL-023
  • L4-POL-024
  • L4-POL-025
  • L4-POL-026
  • L4-POL-027
  • L4-POL-028
  • L4-POL-029
  • L4-POL-030
Temporal scope (start date - end date)
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
2014
2014
2014
2014
2014
2014
2014
2014
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
Yearly
Yearly
Yearly
Yearly
Monitoring type
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
Monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total alkalinity
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • Other monitoring method
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Manual for monitoring in COMBINE programme
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
Monitoring method other
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf
Quality control
according HELCOM recommendations
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according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
according HELCOM recommendations
Data management
Data access
Related indicator/name
Contact
References