Member State report / Art11 / 2020 / D4 / 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 | D4 Food webs/D1 Ecosystems |
| Member State | Poland |
| Region/subregion | Baltic Sea |
| Reported by | Chief Inspectorate of Environmental Protection |
| Report date | 2021-12-31 |
| Report access |
Descriptor |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Monitoring strategy description |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
The goal of the Strategy is to use information from the monitoring programmes established within strategies for Descriptors D1 and D6 for all ecosystem groups: mammals, fish, birds, pelagic and benthic habitats as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017 for assessments of the status of marine waters with regard to food webs as outlined in the Commission Decision (EU) 2017/848 of 17 May 2017. The information gathered will also be used to develop assessment methods for food webs the topic which has not been regionally agreed so far |
Coverage of GES criteria |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Gaps and plans |
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Related targets |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Coverage of targets |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Related measures |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Coverage of measures |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Related monitoring programmes |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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-D1.1-01 |
PL-D1.1-01 |
PL-D1.1-01 |
PL-D1.1-01 |
PL-D1.1-01 |
PL-D1.1-02 |
PL-D1.1-02 |
PL-D1.1-02 |
PL-D1.1-02 |
PL-D1.1-02 |
PL-D1.1-02 |
PL-D1.2-01 |
PL-D1.2-02 |
PL-D1.2-02 |
PL-D1.2-02 |
PL-D1.2-03 |
PL-D1.2-03 |
PL-D1.2-03 |
PL-D1.3-01 |
PL-D1.3-01 |
PL-D1.3-01 |
PL-D1.3-01 |
PL-D1.3-01 |
PL-D1.3-01 |
PL-D1.3-01 |
PL-D1.3-01 |
PL-D1.3-02 |
PL-D1.3-02 |
PL-D1.3-02 |
PL-D1.3-02 |
PL-D1.3-02 |
PL-D1.3-02 |
PL-D1.3-03 |
PL-D1.3-03 |
PL-D1.3-03 |
PL-D1.3-03 |
PL-D1.3-03 |
PL-D1.3-03 |
PL-D1.3-04 |
PL-D1.3-04 |
PL-D1.3-04 |
PL-D1.3-04 |
PL-D1.3-04 |
PL-D1.3-04 |
PL-D1.3-04 |
PL-D1.6-01 |
PL-D1.6-01 |
PL-D1.6-01 |
PL-D1.6-01 |
PL-D1.6-02 |
PL-D1.6-02 |
PL-D1.6-02 |
PL-D1.6-02 |
PL-D1.6-02 |
PL-D1.6-02 |
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 |
Mobile species - wintering birds - abundance |
Mobile species - wintering birds - abundance |
Mobile species - wintering birds - abundance |
Mobile species - wintering birds - abundance |
Mobile species - wintering birds - abundance |
Mobile species - breeding seabirds - distribution and abundance |
Mobile species - breeding seabirds - distribution and abundance |
Mobile species - breeding seabirds - distribution and abundance |
Mobile species - breeding seabirds - distribution and abundance |
Mobile species - breeding seabirds - distribution and abundance |
Mobile species - breeding seabirds - distribution and abundance |
Mobile species – Harbour porpoise - distribution, density |
Mobile species – Grey seal - distribution, abundance, reproduction |
Mobile species – Grey seal - distribution, abundance, reproduction |
Mobile species – Grey seal - distribution, abundance, reproduction |
Mobile species – Harbour seal - distribution, abundance, reproduction |
Mobile species – Harbour seal - distribution, abundance, reproduction |
Mobile species – Harbour seal - distribution, abundance, reproduction |
Mobile species - fish of the deep-water zone |
Mobile species - fish of the deep-water zone |
Mobile species - fish of the deep-water zone |
Mobile species - fish of the deep-water zone |
Mobile species - fish of the deep-water zone |
Mobile species - fish of the deep-water zone |
Mobile species - fish of the deep-water zone |
Mobile species - fish of the deep-water zone |
Mobile species – fish of transitional waters |
Mobile species – fish of transitional waters |
Mobile species – fish of transitional waters |
Mobile species – fish of transitional waters |
Mobile species – fish of transitional waters |
Mobile species – fish of transitional waters |
Mobile species – coastal fish |
Mobile species – coastal fish |
Mobile species – coastal fish |
Mobile species – coastal fish |
Mobile species – coastal fish |
Mobile species – coastal fish |
Mobile species – shallow water fish |
Mobile species – shallow water fish |
Mobile species – shallow water fish |
Mobile species – shallow water fish |
Mobile species – shallow water fish |
Mobile species – shallow water fish |
Mobile species – shallow water fish |
Pelagic habitats - community characteristics |
Pelagic habitats - community characteristics |
Pelagic habitats - community characteristics |
Pelagic habitats - community characteristics |
Plankton blooms (biomass, frequency) |
Plankton blooms (biomass, frequency) |
Plankton blooms (biomass, frequency) |
Plankton blooms (biomass, frequency) |
Plankton blooms (biomass, frequency) |
Plankton blooms (biomass, frequency) |
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 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
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 is carried out to meet the requirements of the Birds Directive as well as the Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017 for Descriptor D1. The results of the monitoring are also used for the work of the HELCOM group. |
Monitoring is carried out to meet the requirements of the Birds Directive as well as the Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017 for Descriptor D1. The results of the monitoring are also used for the work of the HELCOM group. |
Monitoring is carried out to meet the requirements of the Birds Directive as well as the Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017 for Descriptor D1. The results of the monitoring are also used for the work of the HELCOM group. |
Monitoring is carried out to meet the requirements of the Birds Directive as well as the Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017 for Descriptor D1. The results of the monitoring are also used for the work of the HELCOM group. |
Monitoring is carried out to meet the requirements of the Birds Directive as well as the Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017 for Descriptor D1. The results of the monitoring are also used for the work of the HELCOM group. |
So far, three species have been monitored under this program: Cormorant, Sandwich Tern, and Dunlin. New species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oystercatcher, and Shelduck. |
So far, three species have been monitored under this program: Cormorant, Sandwich Tern, and Dunlin. New species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oystercatcher, and Shelduck. |
So far, three species have been monitored under this program: Cormorant, Sandwich Tern, and Dunlin. New species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oystercatcher, and Shelduck. |
So far, three species have been monitored under this program: Cormorant, Sandwich Tern, and Dunlin. New species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oystercatcher, and Shelduck. |
So far, three species have been monitored under this program: Cormorant, Sandwich Tern, and Dunlin. New species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oystercatcher, and Shelduck. |
So far, three species have been monitored under this program: Cormorant, Sandwich Tern, and Dunlin. New species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oystercatcher, and Shelduck. |
Harbour porpoise will be monitored at three locations including two monitored in 2016-2018, i.e. Pomeranian Bay and Ławica Stilo and at one new location - Gulf of Gdańsk. In the case of Pomeranian Bay location all five monitoring stations will be deployed in the same locations as in the pilot research and SAMBAH project. In the case of Ławica Stilo location 4 monitoring stations will be identical to the ones from the pilot monitoring and SAMBAH project. The locations of the 5th station will be subject to the approval of Maritime Office. In the case of the Gulf of Gdańsk location, four stations will be equivalent of those designated within the SAMBAH project, while one station (station code: CPOD15) will be designated in the Puck Bay region, taking into account the specificities of this area (fisheries, shipping, tourism) and in agreement with maritime administration.
In order to maintain regional coherence, the timeline for harbour porpoise monitoring should be compliant with the recommendations of the expert group on marine mammals HELCOM EXPERT GROUP ON MARINE MAMMALS – HELCOM EG MAMA (former name of the group - HELCOM SEAL), which are currently in the consultation stage.
According to the recommendations of the HELCOM MAMA group the monitoring will be performed in accordance with one of two proposed methodologies. One methodology recommends to conduct monitoring for at least 24 months over the six-year period covered by the assessment, but not earlier than 3 years after the end of the previous monitoring. The second methodology recommends to conduct monitoring twice over a six-year period, each of research should last 12 months. The monitoring was planned in accordance with the initial recommendation of this group, i.e. 1 year of measurements every 3 years (HELCOM 2018).
Currently the SAMBAH II project is in the planning stage, the project will cover the entire Baltic Sea area. At the time of development of the current update of the monitoring programme the starting date of research is not known. It is subject to the submission of an application to LIFE funding instrument for the 2021-2027 funding period for the funding of SAMABAH II project. The monitoring planned under SAMBAH II will include the area covered by the SAMBAH project and will be extended to research of areas deeper than 80 m. Within the SAMBAH II project, it is also planned to identify juveniles. To this end, within the implementation of one of the tasks of SAMBAH II, a model will be adapt |
Monitoring of grey seal in Polish Marine Areas will be carried out each year, during which performed observations will allow to detect potential reproduction of this species and determine the abundance of the population from Vistula Mouth - Przekop (the only confirmed haul-out site on the Polish coast, determined at the time of the development of current update of the monitoring programme of marine waters). In the case of determination and confirmation of a new haul-out site during the current monitoring programme of marine waters it will be included in the monitoring.
Monitoring of grey seal will be carried out in accordance with the recommendations contained in the document of the HELCOM MAMA expert group "Guidelines to the monitoring of seals" (HELCOM 2018) and the latest edition of the guideline for the monitoring of grey seal, posted on the Chief Inspectorate of Environmental Protection website in a subpage dedicated to monitoring of marine species and habitat (http://morskiesiedliska.gios.gov.pl/pl/do-pobrania/przewodniki-metodyczne). In the case of aircraft surveys, the methodology contained in the above documents will be used. |
Monitoring of grey seal in Polish Marine Areas will be carried out each year, during which performed observations will allow to detect potential reproduction of this species and determine the abundance of the population from Vistula Mouth - Przekop (the only confirmed haul-out site on the Polish coast, determined at the time of the development of current update of the monitoring programme of marine waters). In the case of determination and confirmation of a new haul-out site during the current monitoring programme of marine waters it will be included in the monitoring.
Monitoring of grey seal will be carried out in accordance with the recommendations contained in the document of the HELCOM MAMA expert group "Guidelines to the monitoring of seals" (HELCOM 2018) and the latest edition of the guideline for the monitoring of grey seal, posted on the Chief Inspectorate of Environmental Protection website in a subpage dedicated to monitoring of marine species and habitat (http://morskiesiedliska.gios.gov.pl/pl/do-pobrania/przewodniki-metodyczne). In the case of aircraft surveys, the methodology contained in the above documents will be used. |
Monitoring of grey seal in Polish Marine Areas will be carried out each year, during which performed observations will allow to detect potential reproduction of this species and determine the abundance of the population from Vistula Mouth - Przekop (the only confirmed haul-out site on the Polish coast, determined at the time of the development of current update of the monitoring programme of marine waters). In the case of determination and confirmation of a new haul-out site during the current monitoring programme of marine waters it will be included in the monitoring.
Monitoring of grey seal will be carried out in accordance with the recommendations contained in the document of the HELCOM MAMA expert group "Guidelines to the monitoring of seals" (HELCOM 2018) and the latest edition of the guideline for the monitoring of grey seal, posted on the Chief Inspectorate of Environmental Protection website in a subpage dedicated to monitoring of marine species and habitat (http://morskiesiedliska.gios.gov.pl/pl/do-pobrania/przewodniki-metodyczne). In the case of aircraft surveys, the methodology contained in the above documents will be used. |
Monitoring of harbour seal is carried out in parallel with the monitoring of grey seal, i.e. the collection of information on the occurrence of harbour seal takes place during the monitoring of grey seal. In addition, in each monitoring year, one observation flight will be performed in August, i.e. during the harbour seal moulting period. The monitoring of harbour seal will include species identification of the other two seal species that may occur on the Polish coast, i.e. grey seal (constantly present) and ringed seal (occasionally occurring).
Monitoring of harbour seal will be carried out in accordance with the recommendations of the HELCOM MAMA expert group contained in the document "Guidelines to the monitoring of seals" (HELCOM 2018) and the latest edition of the guideline for the monitoring of harbour seal, posted on the Chief Inspectorate of Environmental Protection website in a subpage dedicated to monitoring of marine species and habitat (http://morskiesiedliska.gios.gov.pl/pl/do-pobrania/przewodniki-metodyczne). The research will be carried out in accordance with the conditions described in the permits of relevant offices. |
Monitoring of harbour seal is carried out in parallel with the monitoring of grey seal, i.e. the collection of information on the occurrence of harbour seal takes place during the monitoring of grey seal. In addition, in each monitoring year, one observation flight will be performed in August, i.e. during the harbour seal moulting period. The monitoring of harbour seal will include species identification of the other two seal species that may occur on the Polish coast, i.e. grey seal (constantly present) and ringed seal (occasionally occurring).
Monitoring of harbour seal will be carried out in accordance with the recommendations of the HELCOM MAMA expert group contained in the document "Guidelines to the monitoring of seals" (HELCOM 2018) and the latest edition of the guideline for the monitoring of harbour seal, posted on the Chief Inspectorate of Environmental Protection website in a subpage dedicated to monitoring of marine species and habitat (http://morskiesiedliska.gios.gov.pl/pl/do-pobrania/przewodniki-metodyczne). The research will be carried out in accordance with the conditions described in the permits of relevant offices. |
Monitoring of harbour seal is carried out in parallel with the monitoring of grey seal, i.e. the collection of information on the occurrence of harbour seal takes place during the monitoring of grey seal. In addition, in each monitoring year, one observation flight will be performed in August, i.e. during the harbour seal moulting period. The monitoring of harbour seal will include species identification of the other two seal species that may occur on the Polish coast, i.e. grey seal (constantly present) and ringed seal (occasionally occurring).
Monitoring of harbour seal will be carried out in accordance with the recommendations of the HELCOM MAMA expert group contained in the document "Guidelines to the monitoring of seals" (HELCOM 2018) and the latest edition of the guideline for the monitoring of harbour seal, posted on the Chief Inspectorate of Environmental Protection website in a subpage dedicated to monitoring of marine species and habitat (http://morskiesiedliska.gios.gov.pl/pl/do-pobrania/przewodniki-metodyczne). The research will be carried out in accordance with the conditions described in the permits of relevant offices. |
The ichthyological monitoring of the Polish Exclusive Economic Zone in the deepwater zone of Polish marine area has been carried out as a part of national environmental monitoring since 2011, based on data from BITS (Baltic International Trawl Surveys). BITS consist of cruises of particular Baltic countries being temporally and spatially coordinated by ICES. BITS methodology establishes use of standarized bottom trawl of the same design for scientific catches and use of the same research method for hauling sites sampling, data collection and uploading of collected data to the ICES common database - DATRAS, supplemented with measurement and ichthyological analysis of all fish species (including non-commercial). |
The ichthyological monitoring of the Polish Exclusive Economic Zone in the deepwater zone of Polish marine area has been carried out as a part of national environmental monitoring since 2011, based on data from BITS (Baltic International Trawl Surveys). BITS consist of cruises of particular Baltic countries being temporally and spatially coordinated by ICES. BITS methodology establishes use of standarized bottom trawl of the same design for scientific catches and use of the same research method for hauling sites sampling, data collection and uploading of collected data to the ICES common database - DATRAS, supplemented with measurement and ichthyological analysis of all fish species (including non-commercial). |
The ichthyological monitoring of the Polish Exclusive Economic Zone in the deepwater zone of Polish marine area has been carried out as a part of national environmental monitoring since 2011, based on data from BITS (Baltic International Trawl Surveys). BITS consist of cruises of particular Baltic countries being temporally and spatially coordinated by ICES. BITS methodology establishes use of standarized bottom trawl of the same design for scientific catches and use of the same research method for hauling sites sampling, data collection and uploading of collected data to the ICES common database - DATRAS, supplemented with measurement and ichthyological analysis of all fish species (including non-commercial). |
The ichthyological monitoring of the Polish Exclusive Economic Zone in the deepwater zone of Polish marine area has been carried out as a part of national environmental monitoring since 2011, based on data from BITS (Baltic International Trawl Surveys). BITS consist of cruises of particular Baltic countries being temporally and spatially coordinated by ICES. BITS methodology establishes use of standarized bottom trawl of the same design for scientific catches and use of the same research method for hauling sites sampling, data collection and uploading of collected data to the ICES common database - DATRAS, supplemented with measurement and ichthyological analysis of all fish species (including non-commercial). |
The ichthyological monitoring of the Polish Exclusive Economic Zone in the deepwater zone of Polish marine area has been carried out as a part of national environmental monitoring since 2011, based on data from BITS (Baltic International Trawl Surveys). BITS consist of cruises of particular Baltic countries being temporally and spatially coordinated by ICES. BITS methodology establishes use of standarized bottom trawl of the same design for scientific catches and use of the same research method for hauling sites sampling, data collection and uploading of collected data to the ICES common database - DATRAS, supplemented with measurement and ichthyological analysis of all fish species (including non-commercial). |
The ichthyological monitoring of the Polish Exclusive Economic Zone in the deepwater zone of Polish marine area has been carried out as a part of national environmental monitoring since 2011, based on data from BITS (Baltic International Trawl Surveys). BITS consist of cruises of particular Baltic countries being temporally and spatially coordinated by ICES. BITS methodology establishes use of standarized bottom trawl of the same design for scientific catches and use of the same research method for hauling sites sampling, data collection and uploading of collected data to the ICES common database - DATRAS, supplemented with measurement and ichthyological analysis of all fish species (including non-commercial). |
The ichthyological monitoring of the Polish Exclusive Economic Zone in the deepwater zone of Polish marine area has been carried out as a part of national environmental monitoring since 2011, based on data from BITS (Baltic International Trawl Surveys). BITS consist of cruises of particular Baltic countries being temporally and spatially coordinated by ICES. BITS methodology establishes use of standarized bottom trawl of the same design for scientific catches and use of the same research method for hauling sites sampling, data collection and uploading of collected data to the ICES common database - DATRAS, supplemented with measurement and ichthyological analysis of all fish species (including non-commercial). |
The ichthyological monitoring of the Polish Exclusive Economic Zone in the deepwater zone of Polish marine area has been carried out as a part of national environmental monitoring since 2011, based on data from BITS (Baltic International Trawl Surveys). BITS consist of cruises of particular Baltic countries being temporally and spatially coordinated by ICES. BITS methodology establishes use of standarized bottom trawl of the same design for scientific catches and use of the same research method for hauling sites sampling, data collection and uploading of collected data to the ICES common database - DATRAS, supplemented with measurement and ichthyological analysis of all fish species (including non-commercial). |
Monitoring in transitional waterbodies is carried out once every 3 years, except for Puck Lagoon, Vistula Lagoon and Puck Bay, where monitoring is conducted annually. Fish monitoring in transitional waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of transitional waters. |
Monitoring in transitional waterbodies is carried out once every 3 years, except for Puck Lagoon, Vistula Lagoon and Puck Bay, where monitoring is conducted annually. Fish monitoring in transitional waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of transitional waters. |
Monitoring in transitional waterbodies is carried out once every 3 years, except for Puck Lagoon, Vistula Lagoon and Puck Bay, where monitoring is conducted annually. Fish monitoring in transitional waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of transitional waters. |
Monitoring in transitional waterbodies is carried out once every 3 years, except for Puck Lagoon, Vistula Lagoon and Puck Bay, where monitoring is conducted annually. Fish monitoring in transitional waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of transitional waters. |
Monitoring in transitional waterbodies is carried out once every 3 years, except for Puck Lagoon, Vistula Lagoon and Puck Bay, where monitoring is conducted annually. Fish monitoring in transitional waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of transitional waters. |
Monitoring in transitional waterbodies is carried out once every 3 years, except for Puck Lagoon, Vistula Lagoon and Puck Bay, where monitoring is conducted annually. Fish monitoring in transitional waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of transitional waters. |
Fish monitoring in coastal waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of coastal waters. |
Fish monitoring in coastal waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of coastal waters. |
Fish monitoring in coastal waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of coastal waters. |
Fish monitoring in coastal waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of coastal waters. |
Fish monitoring in coastal waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of coastal waters. |
Fish monitoring in coastal waterbodies includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters necessary for assessing the ecological status of coastal waters. |
Fish monitoring in offshore shallow water areas includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters. |
Fish monitoring in offshore shallow water areas includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters. |
Fish monitoring in offshore shallow water areas includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters. |
Fish monitoring in offshore shallow water areas includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters. |
Fish monitoring in offshore shallow water areas includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters. |
Fish monitoring in offshore shallow water areas includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters. |
Fish monitoring in offshore shallow water areas includes an analysis of the following elements:
• determination of weight and abundance of all fish species present in the catch;
• ichthyological analysis of a representative sample of all fish species present in the catch, taking into account their length, individual weight, sex, gonad maturity stage, stomach degree fullness and age of individual fish.
The monitoring also includes the analysis of physico-chemical water parameters. |
Monitoring programme of pelagic habitats – community characteristics includes the determination of the characteristics and variability of phytoplankton and zooplankton communities in PMA. Monitoring is carried out annually in 10 locations in accordance with the HELCOM guidelines. 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 programme of pelagic habitats – community characteristics includes the determination of the characteristics and variability of phytoplankton and zooplankton communities in PMA. Monitoring is carried out annually in 10 locations in accordance with the HELCOM guidelines. 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 programme of pelagic habitats – community characteristics includes the determination of the characteristics and variability of phytoplankton and zooplankton communities in PMA. Monitoring is carried out annually in 10 locations in accordance with the HELCOM guidelines. 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 programme of pelagic habitats – community characteristics includes the determination of the characteristics and variability of phytoplankton and zooplankton communities in PMA. Monitoring is carried out annually in 10 locations in accordance with the HELCOM guidelines. For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. |
In scope of phytoplankton blooms, data on frequency and extent of blooms collected within the monitoring programme of pelagic habitats – community characteristics will be supplemented with information on chlorophyll a concentration in the water column collected from 23 stations located in PMA. The frequency of measurements is 6 times a year except for high frequency station (ZP6) which should be sampled 12 times a year. Data on phytoplankton blooms and chlorophyll a concentration will be supplemented with available open source remote sensing products (from satellite systems). For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. |
In scope of phytoplankton blooms, data on frequency and extent of blooms collected within the monitoring programme of pelagic habitats – community characteristics will be supplemented with information on chlorophyll a concentration in the water column collected from 23 stations located in PMA. The frequency of measurements is 6 times a year except for high frequency station (ZP6) which should be sampled 12 times a year. Data on phytoplankton blooms and chlorophyll a concentration will be supplemented with available open source remote sensing products (from satellite systems). For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. |
In scope of phytoplankton blooms, data on frequency and extent of blooms collected within the monitoring programme of pelagic habitats – community characteristics will be supplemented with information on chlorophyll a concentration in the water column collected from 23 stations located in PMA. The frequency of measurements is 6 times a year except for high frequency station (ZP6) which should be sampled 12 times a year. Data on phytoplankton blooms and chlorophyll a concentration will be supplemented with available open source remote sensing products (from satellite systems). For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. |
In scope of phytoplankton blooms, data on frequency and extent of blooms collected within the monitoring programme of pelagic habitats – community characteristics will be supplemented with information on chlorophyll a concentration in the water column collected from 23 stations located in PMA. The frequency of measurements is 6 times a year except for high frequency station (ZP6) which should be sampled 12 times a year. Data on phytoplankton blooms and chlorophyll a concentration will be supplemented with available open source remote sensing products (from satellite systems). For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. |
In scope of phytoplankton blooms, data on frequency and extent of blooms collected within the monitoring programme of pelagic habitats – community characteristics will be supplemented with information on chlorophyll a concentration in the water column collected from 23 stations located in PMA. The frequency of measurements is 6 times a year except for high frequency station (ZP6) which should be sampled 12 times a year. Data on phytoplankton blooms and chlorophyll a concentration will be supplemented with available open source remote sensing products (from satellite systems). For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection. |
In scope of phytoplankton blooms, data on frequency and extent of blooms collected within the monitoring programme of pelagic habitats – community characteristics will be supplemented with information on chlorophyll a concentration in the water column collected from 23 stations located in PMA. The frequency of measurements is 6 times a year except for high frequency station (ZP6) which should be sampled 12 times a year. Data on phytoplankton blooms and chlorophyll a concentration will be supplemented with available open source remote sensing products (from satellite systems). 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 purpose |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Other policies and conventions |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||||||||||||||||||||||||||||||||||||||
Regional cooperation - coordinating body |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||||||
Regional cooperation - countries involved |
DE,DK,EE,FI,LT,LV,PL,SE |
DE,DK,EE,FI,LT,LV,PL,SE |
DE,DK,EE,FI,LT,LV,PL,SE |
DE,DK,EE,FI,LT,LV,PL,SE |
DE,DK,EE,FI,LT,LV,PL,SE |
DE,DK,EE,FI,LT,LV,PL,SE |
DE,DK,EE,FI,LT,LV,PL,SE |
DE,DK,EE,FI,LT,LV,PL,SE |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Regional cooperation - implementation level |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Monitoring details |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
1) Offshore Wintering Marine Birds Survey. Offshore survey dedicated to wintering waterbirds on Baltic open marine waters. 56 line transects. One field visit each year in January. Two observers on two sides of the ship counting all birds using distance sampling and snapshot methodology.
2) Transitional Waters Wintering Waterbird Survey. Mid-January count of all birds occurring in 31 sites covering transitional waters. The study takes place using the generally accepted methodology recommended by Wetland International during the International Waterbird Census. Most of the area is counted from the shore - the observer counts the birds seen along the designated section. Large water bodies such as coastal lagoons are counted using an aircraft, a drone, or a boat. |
1) Offshore Wintering Marine Birds Survey. Offshore survey dedicated to wintering waterbirds on Baltic open marine waters. 56 line transects. One field visit each year in January. Two observers on two sides of the ship counting all birds using distance sampling and snapshot methodology.
2) Transitional Waters Wintering Waterbird Survey. Mid-January count of all birds occurring in 31 sites covering transitional waters. The study takes place using the generally accepted methodology recommended by Wetland International during the International Waterbird Census. Most of the area is counted from the shore - the observer counts the birds seen along the designated section. Large water bodies such as coastal lagoons are counted using an aircraft, a drone, or a boat. |
1) Offshore Wintering Marine Birds Survey. Offshore survey dedicated to wintering waterbirds on Baltic open marine waters. 56 line transects. One field visit each year in January. Two observers on two sides of the ship counting all birds using distance sampling and snapshot methodology.
2) Transitional Waters Wintering Waterbird Survey. Mid-January count of all birds occurring in 31 sites covering transitional waters. The study takes place using the generally accepted methodology recommended by Wetland International during the International Waterbird Census. Most of the area is counted from the shore - the observer counts the birds seen along the designated section. Large water bodies such as coastal lagoons are counted using an aircraft, a drone, or a boat. |
1) Offshore Wintering Marine Birds Survey. Offshore survey dedicated to wintering waterbirds on Baltic open marine waters. 56 line transects. One field visit each year in January. Two observers on two sides of the ship counting all birds using distance sampling and snapshot methodology.
2) Transitional Waters Wintering Waterbird Survey. Mid-January count of all birds occurring in 31 sites covering transitional waters. The study takes place using the generally accepted methodology recommended by Wetland International during the International Waterbird Census. Most of the area is counted from the shore - the observer counts the birds seen along the designated section. Large water bodies such as coastal lagoons are counted using an aircraft, a drone, or a boat. |
1) Offshore Wintering Marine Birds Survey. Offshore survey dedicated to wintering waterbirds on Baltic open marine waters. 56 line transects. One field visit each year in January. Two observers on two sides of the ship counting all birds using distance sampling and snapshot methodology.
2) Transitional Waters Wintering Waterbird Survey. Mid-January count of all birds occurring in 31 sites covering transitional waters. The study takes place using the generally accepted methodology recommended by Wetland International during the International Waterbird Census. Most of the area is counted from the shore - the observer counts the birds seen along the designated section. Large water bodies such as coastal lagoons are counted using an aircraft, a drone, or a boat. |
Census 3 species Sterna sandvicensis, Phalacrocorax carbo and Calidris alpina in coastal zone. Sterna sandvicensis, Phalacrocorax carbo: all nests are counted in active breeding colonies. Calidris alpina: extincted in Poland, but during the fieldwork observers search for birds in historic breeding sites. Four new species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oysterctcher and Shelduck. The methodology consists in monitoring known species siteds and determining number of pairs based on the highest established breeding category. |
Census 3 species Sterna sandvicensis, Phalacrocorax carbo and Calidris alpina in coastal zone. Sterna sandvicensis, Phalacrocorax carbo: all nests are counted in active breeding colonies. Calidris alpina: extincted in Poland, but during the fieldwork observers search for birds in historic breeding sites. Four new species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oysterctcher and Shelduck. The methodology consists in monitoring known species siteds and determining number of pairs based on the highest established breeding category. |
Census 3 species Sterna sandvicensis, Phalacrocorax carbo and Calidris alpina in coastal zone. Sterna sandvicensis, Phalacrocorax carbo: all nests are counted in active breeding colonies. Calidris alpina: extincted in Poland, but during the fieldwork observers search for birds in historic breeding sites. Four new species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oysterctcher and Shelduck. The methodology consists in monitoring known species siteds and determining number of pairs based on the highest established breeding category. |
Census 3 species Sterna sandvicensis, Phalacrocorax carbo and Calidris alpina in coastal zone. Sterna sandvicensis, Phalacrocorax carbo: all nests are counted in active breeding colonies. Calidris alpina: extincted in Poland, but during the fieldwork observers search for birds in historic breeding sites. Four new species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oysterctcher and Shelduck. The methodology consists in monitoring known species siteds and determining number of pairs based on the highest established breeding category. |
Census 3 species Sterna sandvicensis, Phalacrocorax carbo and Calidris alpina in coastal zone. Sterna sandvicensis, Phalacrocorax carbo: all nests are counted in active breeding colonies. Calidris alpina: extincted in Poland, but during the fieldwork observers search for birds in historic breeding sites. Four new species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oysterctcher and Shelduck. The methodology consists in monitoring known species siteds and determining number of pairs based on the highest established breeding category. |
Census 3 species Sterna sandvicensis, Phalacrocorax carbo and Calidris alpina in coastal zone. Sterna sandvicensis, Phalacrocorax carbo: all nests are counted in active breeding colonies. Calidris alpina: extincted in Poland, but during the fieldwork observers search for birds in historic breeding sites. Four new species have been added to the monitoring program since 2020: Ringed Plover, Little Tern, Oysterctcher and Shelduck. The methodology consists in monitoring known species siteds and determining number of pairs based on the highest established breeding category. |
24 months of continuous monitoring every 6 years (since the beginning of previous monitoring) or 12 months of continuous monitoring twice in the 6-year period. In addition, the occurrence of young individuals will be included in the monitoring in future in line with the SAMBAH II project, which will estimate not only the density but also the number of individuals. |
Aerial observations during the breeding season (February-March) and during the moulting period (May-June), in the identified haul-out sites of this species will be carried out using unmanned aircraft equipped with a high-resolution video camera or camera, allowing for determination of the species composition of the group and number of individuals resting on sandbanks and surrounding waters. The flight should take place at a distance (about 150 m from each of the islands or sandbanks) at a ceiling of about 100 – 150 m from the resting place. It is recommended to avoid direct flights over the occupied haul-out sites in order to prevent disturbance of animals. Photos should be taken while hovering. The number of flights is determined by the current conditions and the research permits obtained, but it is recommended to perform no more than two flights during one day of monitoring.
During the flights, individuals of the other two seal species occurring on the Polish coast will be identified and counted, i.e. rare harbour seal and occasionally occurring ringed seal. |
Aerial observations during the breeding season (February-March) and during the moulting period (May-June), in the identified haul-out sites of this species will be carried out using unmanned aircraft equipped with a high-resolution video camera or camera, allowing for determination of the species composition of the group and number of individuals resting on sandbanks and surrounding waters. The flight should take place at a distance (about 150 m from each of the islands or sandbanks) at a ceiling of about 100 – 150 m from the resting place. It is recommended to avoid direct flights over the occupied haul-out sites in order to prevent disturbance of animals. Photos should be taken while hovering. The number of flights is determined by the current conditions and the research permits obtained, but it is recommended to perform no more than two flights during one day of monitoring.
During the flights, individuals of the other two seal species occurring on the Polish coast will be identified and counted, i.e. rare harbour seal and occasionally occurring ringed seal. |
Aerial observations during the breeding season (February-March) and during the moulting period (May-June), in the identified haul-out sites of this species will be carried out using unmanned aircraft equipped with a high-resolution video camera or camera, allowing for determination of the species composition of the group and number of individuals resting on sandbanks and surrounding waters. The flight should take place at a distance (about 150 m from each of the islands or sandbanks) at a ceiling of about 100 – 150 m from the resting place. It is recommended to avoid direct flights over the occupied haul-out sites in order to prevent disturbance of animals. Photos should be taken while hovering. The number of flights is determined by the current conditions and the research permits obtained, but it is recommended to perform no more than two flights during one day of monitoring.
During the flights, individuals of the other two seal species occurring on the Polish coast will be identified and counted, i.e. rare harbour seal and occasionally occurring ringed seal. |
Aerial observations during moulting season (August) will be performed along the entire Polish coast, including the flight over Ryf Mew, over the sandbanks in the Vistula River mouth in the Mewia Łacha Reserve and over the jetties of the Vistula river mouth. Observations and photographic documentation will be performed from the deck of an aircraft, that will fly over the entire location (Polish coast with the abovementioned Ryf Mew, sandbanks and jetties of the Vistula river mouth) during one day. Flight standards will be consistent with the flight guideline and the decisions and permits issued by the competent institutions and offices. Ground observations will be performed at sites where no permit for monitoring and observations from the aircraft is obtained. Both during the flights and ground observations, all observed individuals of seals will be recorded. Individuals of harbour, grey and ringed seals will be recorded and photographed. The number of juveniles and adults will be recorded. Observations of the habitat status will be made in order to perform the assessment of the species in accordance with the Habitats Directive. |
Aerial observations during moulting season (August) will be performed along the entire Polish coast, including the flight over Ryf Mew, over the sandbanks in the Vistula River mouth in the Mewia Łacha Reserve and over the jetties of the Vistula river mouth. Observations and photographic documentation will be performed from the deck of an aircraft, that will fly over the entire location (Polish coast with the abovementioned Ryf Mew, sandbanks and jetties of the Vistula river mouth) during one day. Flight standards will be consistent with the flight guideline and the decisions and permits issued by the competent institutions and offices. Ground observations will be performed at sites where no permit for monitoring and observations from the aircraft is obtained. Both during the flights and ground observations, all observed individuals of seals will be recorded. Individuals of harbour, grey and ringed seals will be recorded and photographed. The number of juveniles and adults will be recorded. Observations of the habitat status will be made in order to perform the assessment of the species in accordance with the Habitats Directive. |
Aerial observations during moulting season (August) will be performed along the entire Polish coast, including the flight over Ryf Mew, over the sandbanks in the Vistula River mouth in the Mewia Łacha Reserve and over the jetties of the Vistula river mouth. Observations and photographic documentation will be performed from the deck of an aircraft, that will fly over the entire location (Polish coast with the abovementioned Ryf Mew, sandbanks and jetties of the Vistula river mouth) during one day. Flight standards will be consistent with the flight guideline and the decisions and permits issued by the competent institutions and offices. Ground observations will be performed at sites where no permit for monitoring and observations from the aircraft is obtained. Both during the flights and ground observations, all observed individuals of seals will be recorded. Individuals of harbour, grey and ringed seals will be recorded and photographed. The number of juveniles and adults will be recorded. Observations of the habitat status will be made in order to perform the assessment of the species in accordance with the Habitats Directive. |
Data collected 5 times a year in deep and shallow water zones. One high frequency station sampled 12 times a year. |
Data collected 5 times a year in deep and shallow water zones. One high frequency station sampled 12 times a year. |
Data collected 5 times a year in deep and shallow water zones. One high frequency station sampled 12 times a year. |
Data collected 5 times a year in deep and shallow water zones. One high frequency station sampled 12 times a year. |
|||||||||||||||||||||||||||||||||
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
|
Benthic-feeding birds
|
Grazing birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Wading birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Wading birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Wading birds
|
Small toothed cetaceans
|
Seals
|
Seals
|
Seals
|
Seals
|
Seals
|
Seals
|
Demersal shelf fish
|
Established non-indigenous species
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Shelf ecosystems
|
Established non-indigenous species
|
Established non-indigenous species
|
Shelf ecosystems
|
Shelf ecosystems
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Coastal fish
|
Coastal fish
|
Established non-indigenous species
|
Established non-indigenous species
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Demersal shelf fish
|
Established non-indigenous species
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Other pelagic habitats
|
Other pelagic habitats
|
Other pelagic habitats
|
Other pelagic habitats
|
Other pelagic habitats
|
Other pelagic habitats
|
Eutrophication
|
Eutrophication
|
Eutrophication
|
Eutrophication
|
Elements |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
GES criteria |
D5C6 |
D5C6 |
D5C7 |
D5C7 |
D5C8 |
D5C8 |
D6C5 |
D6C5 |
D5C6 |
D5C6 |
D5C7 |
D5C7 |
D5C8 |
D5C8 |
D6C5 |
D6C5 |
NotRelevan |
NotRelevan |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C4 |
D1C4 |
D1C4 |
D1C2 |
D1C2 |
D1C3 |
D1C4 |
D1C2 |
D1C3 |
D1C4 |
D1C3 |
D2C2 |
D3C1 |
D3C1 |
D3C2 |
D3C2 |
D3C3 |
D4C3 |
D2C2 |
D2C2 |
D4C1 |
D4C1 |
NotRelevan |
NotRelevan |
D1C2 |
D1C2 |
D2C2 |
D2C2 |
NotRelevan |
NotRelevan |
D1C3 |
D2C2 |
D3C1 |
D3C1 |
D3C2 |
D3C2 |
D3C3 |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
D1C6 |
D1C6 |
D5C2 |
D5C2 |
D5C3 |
D5C3 |
Parameters |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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 |
Density |
abundance and biomass |
Reproduction |
abundance and biomass |
Reproduction |
biomass |
catches divided by stock size index |
stock size index from survey |
abundance |
abundance |
catches divided by stock size index |
stock size index from survey |
Abundance and biomass |
abundance and biomass |
Abundance and biomass |
abundance and biomass |
concentration |
concentration |
|||||||||||||||||||||||||||||||||||||||||||||||||||
Spatial scope |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Marine reporting units |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2014-9999 |
2014-9999 |
2014-9999 |
2014-9999 |
2014-9999 |
2014-9999 |
2014-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
2011-9999 |
1999-9999 |
1999-9999 |
1999-9999 |
1999-9999 |
1999-9999 |
1999-9999 |
1999-9999 |
1999-9999 |
1999-9999 |
1999-9999 |
Monitoring frequency |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
6-monthly |
6-monthly |
6-monthly |
6-monthly |
6-monthly |
6-monthly |
6-monthly |
6-monthly |
3-yearly |
3-yearly |
3-yearly |
3-yearly |
3-yearly |
3-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
6-yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Monitoring type |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Monitoring method |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Monitoring method other |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
The HELCOM common monitoring relevant on white-tailed sea eagles is described on a general level in the HELCOM Monitoring Manual in the sub-programme: Marine bird health.
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health |
http://morskiesiedliska.gios.gov.pl/images/1351_Morswin_OST.pdf
Method according to Sambah project based on C-POD passive acoustic detection. |
http://morskiesiedliska.gios.gov.pl/images/1364_Foka_szara_OST.pdf |
http://morskiesiedliska.gios.gov.pl/images/1364_Foka_szara_OST.pdf |
http://morskiesiedliska.gios.gov.pl/images/1364_Foka_szara_OST.pdf |
http://morskiesiedliska.gios.gov.pl/images/1365_Foka_pospolita.pdf |
http://morskiesiedliska.gios.gov.pl/images/1365_Foka_pospolita.pdf |
http://morskiesiedliska.gios.gov.pl/images/1365_Foka_pospolita.pdf |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl Podręcznik do monitoringu elementów biologicznych i klasyfikacji stanu ekologicznego wód powierzchniowych. Aktualizacja metod. (GIOŚ 2020) https://www.gios.gov.pl/images/dokumenty/pms/monitoring_wod/Podrecznik_Monitoringu_Wod.pdf |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl Podręcznik do monitoringu elementów biologicznych i klasyfikacji stanu ekologicznego wód powierzchniowych. Aktualizacja metod. (GIOŚ 2020) https://www.gios.gov.pl/images/dokumenty/pms/monitoring_wod/Podrecznik_Monitoringu_Wod.pdf |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl Podręcznik do monitoringu elementów biologicznych i klasyfikacji stanu ekologicznego wód powierzchniowych. Aktualizacja metod. (GIOŚ 2020) https://www.gios.gov.pl/images/dokumenty/pms/monitoring_wod/Podrecznik_Monitoringu_Wod.pdf |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
Przewodnik metodyczny do badań terenowych i analiz laboratoryjnych ichtiofauny w wodach przejściowych i przybrzeżnych; GIOŚ 2014) www.gios.gov.pl |
|||||||||||||||||||||||||||||||||||||||||
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
|
Two steps: (1) fieldwork organiser keeps sure that fieldwork is going on according to methodological guidelines, (2) national coordinator explore and check the data. |
Two steps: (1) fieldwork organiser keeps sure that fieldwork is going on according to methodological guidelines, (2) national coordinator explore and check the data. |
Two steps: (1) fieldwork organiser keeps sure that fieldwork is going on according to methodological guidelines, (2) national coordinator explore and check the data. |
Two steps: (1) fieldwork organiser keeps sure that fieldwork is going on according to methodological guidelines, (2) national coordinator explore and check the data. |
Two steps: (1) fieldwork organiser keeps sure that fieldwork is going on according to methodological guidelines, (2) national coordinator explore and check the data. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
One step. National coordinator keeps sure that fieldwork is going on according to the methodological standards and is responsible for data validation and results calculation. |
according to Sambah project
|
according to Helcom
|
according to Helcom
|
according to Helcom
|
according to Helcom
|
according to Helcom
|
according to Helcom
|
Screening programme ICES DATRAS centre
|
Screening programme ICES DATRAS centre
|
Screening programme ICES DATRAS centre
|
Screening programme ICES DATRAS centre
|
Screening programme ICES DATRAS centre
|
Screening programme ICES DATRAS centre
|
Screening programme ICES DATRAS centre
|
Screening programme ICES DATRAS centre
|
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
NMFRI provides an internal multi-layer quality control of data collected during sampling e.g: cross-checking the catches protocols, database correctness, working scheme in accordance with agreed HELCOM methodology. |
according HELCOM recommendations
|
according HELCOM recommendations
|
according HELCOM recommendations
|
according HELCOM recommendations
|
according HELCOM recommendations
|
according HELCOM recommendations
|
according HELCOM recommendations
|
according HELCOM recommendations
|
according HELCOM recommendations
|
according HELCOM recommendations
|
Data management |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
Raw databases are stored on the Chief Inspectorate of Environmental Protection hard disks. |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Data access |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Related indicator/name |
|
|
|
|
|
|
|
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Contact |
Person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
National coordinator of monitoring programme: Włodzimierz Meissner: wlodzimierz.meissner@ug.edu.pl , and Dominik Marchowski: marchowskid@gmail.com |
Person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
National coordinator of monitoring programme: Włodzimierz Meissner: wlodzimierz.meissner@ug.edu.pl , and Dominik Marchowski: marchowskid@gmail.com |
Person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
National coordinator of monitoring programme: Włodzimierz Meissner: wlodzimierz.meissner@ug.edu.pl , and Dominik Marchowski: marchowskid@gmail.com |
Person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
National coordinator of monitoring programme: Włodzimierz Meissner: wlodzimierz.meissner@ug.edu.pl , and Dominik Marchowski: marchowskid@gmail.com |
Person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
National coordinator of monitoring programme: Włodzimierz Meissner: wlodzimierz.meissner@ug.edu.pl , and Dominik Marchowski: marchowskid@gmail.com |
A person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
General coordinator of monitoring program: Tomasz Chodkiewicz tomasz.chodkiewicz@otop.org.pl |
A person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
General coordinator of monitoring program: Tomasz Chodkiewicz tomasz.chodkiewicz@otop.org.pl |
A person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
General coordinator of monitoring program: Tomasz Chodkiewicz tomasz.chodkiewicz@otop.org.pl |
A person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
General coordinator of monitoring program: Tomasz Chodkiewicz tomasz.chodkiewicz@otop.org.pl |
A person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
General coordinator of monitoring program: Tomasz Chodkiewicz tomasz.chodkiewicz@otop.org.pl |
A person responsible in Chief Inspectorate of Environmental Protection: Dorota Łukasik d.lukasik@gios.gov.pl
General coordinator of monitoring program: Tomasz Chodkiewicz tomasz.chodkiewicz@otop.org.pl |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
References |