Member State report / Art11 / 2020 / D6 / 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 D6 Sea-floor integrity/D1 Benthic habitats
Member State Poland
Region/subregion Baltic Sea
Reported by Chief Inspectorate of Environmental Protection
Report date 2021-12-31
Report access

Descriptor
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
Monitoring strategy description
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed characteristics. Regional coordination is assured by applying HELCOM monitoring guidelines and assessment strategies.
The goal of the strategy is to gather information on all relevant physical pressures contributing to disturbance and loss of the seafloor resulting from human activities outlined in Commission Directive (EU) 2017/845 of 17 May 2017 as well as on the status and extent of benthic habitats for the criteria laid down in the Commission Decision (EU) 2017/848 of 17 May 2017. Information gathered within the strategy will help to assess impact of human activities by establishing extent of adverse effects on the condition of each habitat type. The programme will provide information both on the status of marine waters as well as on pressures and impacts on benthic habitats. The strategy consists of 5 monitoring programmes: 2 targeted to assess status of benthic habitats and species and 3 to assess physical pressures and changes in seabed 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
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
Related targets
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
  • PL_Target_D6
  • PL_Target_D6C1
  • PL_Target_D6C2
  • PL_Target_D6C2_01
  • PL_Target_D6C2_02
  • PL_Target_D6C3
  • PL_Target_D6C3_01
  • PL_Target_D6C3_02
  • PL_Target_D6C4
  • PL_Target_D6C5
  • PL_Target_D6C5_ESMIz
  • PL_Target_D6C5_SM1
  • PL_Target_D6C5_zoobenthos
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
Related measures
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
  • BALPL-M004 - 'KTM38_1 Research and assessment of necessity of enlargement areas where trawling is banned - including controlling measures'
  • BALPL-M029 - 'KTM27 The introduction of restrictions on bottom trawling in areas where there is a need to protect valuable communities of benthic organisms'
  • BALPL-M030 - 'KTM14_5 Concessions and environmental decisions for projects involving the recognition, exploration and exploitation of offshore deposits (guidelines for authorities issuing administrative decisions)'
  • BALPL-M031 - 'KTM31_3 Use of the results of comprehensive guidelines for site selection of ecosystem methodology depositing sediments (ore faucet) in sea and coastal “dumping sites” management in the Baltic Sea area'
  • BALPL-M034 - 'KTM14_10 Assessment of the extent of environmental hazards resulting from wrecks on the seabed'
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
Related monitoring programmes
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
  • PL-D06-01
  • PL-D06-02
  • PL-D06-03
  • PL-D06-04
  • PL-D06-05
Programme code
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-D06-03
PL-D06-03
PL-D06-04
PL-D06-04
PL-D06-05
PL-D06-05
Programme name
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
Seabed habitats - physical and chemical characteristics
Seabed habitats - physical and chemical characteristics
Physical loss - distribution and extent
Physical loss - distribution and extent
Physical disturbance - distribution and extent
Physical disturbance - distribution and extent
Update type
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
Old programme codes
Programme description
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 parameters in scope of the seabed habitats - physical and chemical characteristics programme includes monitoring of hydromorphological parameters that characterize morphological conditions, morphometric conditions, change in depth and quantitative structure and physical and chemical characteristics of the seabed and is carried out within the WFD waterbodies at measurement points and profiles. Additional supplementary parameters are meteorological data on wind speed and direction at stations and hydrological data on sea levels obtained at stations. Monitoring will be carried out once in the period 2020-2025. In the current water management cycle, covering the period 2016-2021, hydromorphological monitoring was carried out in 2019. Another hydromorphological monitoring is scheduled to be carried out in the next water management cycle, that is, in the period 2022-2027, not later than 6 years after the preceding hydromorphological monitoring is performed in accordance with the Regulation of Minister of maritime economy and inland navigation of 9 October 2019 on the form and method of monitoring of surface water and groundwater bodies (Journal of Laws, item 2147).
Monitoring of parameters in scope of the seabed habitats - physical and chemical characteristics programme includes monitoring of hydromorphological parameters that characterize morphological conditions, morphometric conditions, change in depth and quantitative structure and physical and chemical characteristics of the seabed and is carried out within the WFD waterbodies at measurement points and profiles. Additional supplementary parameters are meteorological data on wind speed and direction at stations and hydrological data on sea levels obtained at stations. Monitoring will be carried out once in the period 2020-2025. In the current water management cycle, covering the period 2016-2021, hydromorphological monitoring was carried out in 2019. Another hydromorphological monitoring is scheduled to be carried out in the next water management cycle, that is, in the period 2022-2027, not later than 6 years after the preceding hydromorphological monitoring is performed in accordance with the Regulation of Minister of maritime economy and inland navigation of 9 October 2019 on the form and method of monitoring of surface water and groundwater bodies (Journal of Laws, item 2147).
The monitoring of parameters for physical loss of the seafloor is carried out indirectly by Chief Inspectorate of Environmental Protection on the basis of data submitted inter alia by the Maritime Offices, which collect information e.g. on the hydrotechnical constructions on the shoreline in transitional and coastal waters and deepening of waterways.
The monitoring of parameters for physical loss of the seafloor is carried out indirectly by Chief Inspectorate of Environmental Protection on the basis of data submitted inter alia by the Maritime Offices, which collect information e.g. on the hydrotechnical constructions on the shoreline in transitional and coastal waters and deepening of waterways.
The monitoring of parameters for physical disturbance of the seafloor is carried out indirectly by Chief Inspectorate of Environmental Protection on the basis of data submitted inter alia by the Maritime Offices. Regarding the determination of the area of the seafloor disturbed by fishing with dredged gear, the data are collected by ICES.
The monitoring of parameters for physical disturbance of the seafloor is carried out indirectly by Chief Inspectorate of Environmental Protection on the basis of data submitted inter alia by the Maritime Offices. Regarding the determination of the area of the seafloor disturbed by fishing with dredged gear, the data are collected by ICES.
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
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
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
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
Agreed data collection methods
Agreed data collection methods
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 list of hydromorphological parameters constitutes of: Morphological conditions: Shore-normal profiles up to 1 NM from the shoreline Parameter (A) Morphometrical conditions: - width of coastal zones - sb, sr, sg (10 m below sea level. and 1 NM) - status of longshore bars – number and section area Change in depth: - behind surf zone - behind breaker zone - 1 NM from the shoreline - the depth of the sampling point Seabed structure and characteristics: - grain size – median of grain diameter - concentration of organic matter - nutrient concentration (Ntot and Ptot) - Chlorophyll a - redox potential (Eh) and pH - concentration of contaminants (Me, WWA, PCB, TBT)
The list of hydromorphological parameters constitutes of: Morphological conditions: Shore-normal profiles up to 1 NM from the shoreline Parameter (A) Morphometrical conditions: - width of coastal zones - sb, sr, sg (10 m below sea level. and 1 NM) - status of longshore bars – number and section area Change in depth: - behind surf zone - behind breaker zone - 1 NM from the shoreline - the depth of the sampling point Seabed structure and characteristics: - grain size – median of grain diameter - concentration of organic matter - nutrient concentration (Ntot and Ptot) - Chlorophyll a - redox potential (Eh) and pH - concentration of contaminants (Me, WWA, PCB, TBT)
Information on shoreline hydrotechnical constructions in transitional and coastal waters e.g.: - the length of sea walls, - number of groynes (length of shore end extent to the sea) - beach nourishment, - anchorages.
Information on shoreline hydrotechnical constructions in transitional and coastal waters e.g.: - the length of sea walls, - number of groynes (length of shore end extent to the sea) - beach nourishment, - anchorages.
The monitoring is based on: Information on the fishing intensity with bottom contacting gear calculated to swept area ratio (SAR). Information on the temporal and spatial extent of activities related with: - deepening of waterways, - disposal of dredged material from deepening of waterways and ports - dredging and other activities impacting surface sediments Information on the temporal and spatial extent of activities related to sand and gravel extraction.
The monitoring is based on: Information on the fishing intensity with bottom contacting gear calculated to swept area ratio (SAR). Information on the temporal and spatial extent of activities related with: - deepening of waterways, - disposal of dredged material from deepening of waterways and ports - dredging and other activities impacting surface sediments Information on the temporal and spatial extent of activities related to sand and gravel extraction.
Features
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
Physical and hydrological characteristics
Physical and hydrological characteristics
Physical loss of the seabed
Physical loss of the seabed
Physical disturbance to seabed
Physical disturbance to seabed
Elements
  • 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
  • Seabed substrate and morphology
  • Seabed substrate and morphology
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
GES criteria
D5C6
D5C6
D5C7
D5C7
D5C8
D5C8
D6C5
D6C5
D5C6
D5C6
D5C7
D5C7
D5C8
D5C8
D6C5
D6C5
NotRelevan
NotRelevan
NotRelevan
NotRelevan
D6C1
D6C1
D6C2
D6C2
Parameters
  • 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
  • Physical structure of habitat (e.g. sediment characteristics, topographic structure)
  • Physical structure of habitat (e.g. sediment characteristics, topographic structure)
  • Extent
  • Extent
  • Extent
  • Extent
Parameter Other
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)
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_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
  • 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
  • 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
  • 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
  • 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
  • BAL-POL-FAO27-3D24
  • BAL-POL-FAO27-3D25
  • BAL-POL-FAO27-3D26
  • 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
  • BAL-POL-FAO27-3D24
  • BAL-POL-FAO27-3D25
  • BAL-POL-FAO27-3D26
  • 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
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
1999-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
2014-9999
Monitoring frequency
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Other
Other
As needed
As needed
Continually
Continually
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 coastal
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
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
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
Monitoring method other
Verified method of monitoring and hydromorphological assessment of transitional and coastal waters (GIOŚ 2018 or its update). www.gios.gov.pl
Verified method of monitoring and hydromorphological assessment of transitional and coastal waters (GIOŚ 2018 or its update). www.gios.gov.pl
Monitoring is based on the information on shoreline changes (parallel and transverse construction, nourishment) collected by Marine Offices
Monitoring is based on the information on shoreline changes (parallel and transverse construction, nourishment) collected by Marine Offices
Information on number, area and length of trawls with bottom contacting gear is collected by ICES. Data on the amount of deposed dredged material from deepening of waterways and ports collected from Marine Offices. Data on the scope of aggregate extraction collected by Competent Minister of Climate.
Information on number, area and length of trawls with bottom contacting gear is collected by ICES. Data on the amount of deposed dredged material from deepening of waterways and ports collected from Marine Offices. Data on the scope of aggregate extraction collected by Competent Minister of Climate.
Quality control
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 to Helcom guidlines.
according to Helcom guidlines.
not relevant
not relevant
not relevant
not relevant
Data management
Data access
Related indicator/name
Contact
References