Member State report / Art14 / 2022 / D6 / Poland / Baltic Sea
Report type | Member State report to Commission |
MSFD Article | Art. 14 Exceptions (and Art. 17 updates) |
Report due | 2022-10-15 |
GES Descriptor | D6 Sea-floor integrity/D1 Benthic habitats |
Member State | Poland |
Region/subregion | Baltic Sea |
Report date | 1900-01-01 |
Report access | 363 |
Marine reporting units |
|
|
|
---|---|---|---|
Region subregion |
Baltic Sea |
Baltic Sea |
Baltic Sea |
Exception code |
PL-E12 |
PL-E13 |
PL-E14 |
Exception old code |
|||
Exception name |
Non-achievement of GES with regard to Descriptor D1 ""Biodiversity - Benthic habitats"" |
Non-achievement of GES with regard to Descriptor D1 ""Biodiversity - Benthic habitats"" |
Non-achievement of GES with regard to Descriptor D1 ""Biodiversity - Benthic habitats"" |
Exception type |
Art. 14(1)(a) |
Art. 14(1)(e) |
Art. 14(1)(d) |
Exception reason |
Action needed by another Member State(s);Action needed by another non-EU state(s) |
Other(e) |
Economic or social activities fulfilling specific obligations of public services |
GES achieved |
2050 |
||
Relevant pressures |
|
|
|
Relevant targets |
|||
GES component |
|
|
|
Relevant features |
|
|
|
Justification description |
The vast majority of Marine Reporting Units were found to represent subGES with regard to benthic communities. This was due to subGES values of the B zoobenthos index as well as subGES values of SM1 and ESMIz macrophyte indexes. The B zoobenthos index has been shown to be strongly dependent on total nitrogen concentrations near the bottom. These concentrations are in turn a manifestation of eutrophication. Macrophyte communities are also known to be dependent on nutrient concentration levels, although the relationships in this case are more complex. Nevertheless, it is clear that lasting improvement of the quality of benthic communities will not be possible without major reductions of nutrient inputs. As explained in the case of Exception XX (Non-achievement of GES with regard to descriptor D5 ""Eutrophication""), the required reductions of nutrient levels in Polish Marine Waters will be impossible without significant efforts on the part of other countries of the Baltic Sea Basin, i.e. Denmark, Estonia, Finland, Germany, Lithuaniam, Latvia, Russia and Sweden, but also Belarus, the Czech Republic and Ukraine. |
The vast majority of Marine Reporting Units were found to represent subGES with regard to benthic communities. This was due to subGES values of the B zoobenthos index as well as subGES values of SM1 and ESMIz macrophyte indexes. The B zoobenthos index has been shown to be strongly dependent on total nitrogen concentrations near the bottom. These concentrations are in turn a manifestation of eutrophication. Macrophyte communities are also known to be dependent on nutrient input levels, although the relationships in this case are more complex. Nevertheless, it is clear that lasting improvement of the quality of benthic communities will not be possible without major reductions of nutrient inputs. As explained in the case of Exception XX (Non-achievement of GES with regard to descriptor D5 ""Eutrophication""), the reqiured reductions of nutrient levels are very unlikely before 2050. |
No EU or regional GES indices have been adopted with regard to physical loss of seabed (D6C1). However, three transitional water bodies of Polish Marine Waters have been found to represent subGES status basing on a national indicator. The reason for the subGES status is existing infrastructure related to, among others, inland navigation, tourism and recreation, fisheries and other interests. Restoration of GES in these water bodies would require the dismantling of some of this infrastructure and would therefore be detrimental to legitimate economic interests of local and regional importance. In some cases, as in the case of the Vistula river mouth, which is actually a man-made outlet built over a century ago, the dismantling of existing hydroengineering structures and restoring the river's original course would not only have serious economic consequences, including greatly increased risk of flooding in Gdansk, but would actually destroy important habitats which currently host a number of threatened bird species and Poland's only grey seal haul-out site. For these reasons, Poland believes restoring GES with regard to criterion D6C1 in the three water bodies concerned would be against public interest. |
Spatial scope geographic zones |
Transitional waters (WFD);Coastal waters (WFD);Territorial waters;EEZ (or similar) |
Transitional waters (WFD);Coastal waters (WFD);Territorial waters;EEZ (or similar) |
Transitional waters (WFD) |
Mitigation |
BALPL-M006 will contribute directly to preventing further deterioration and to achievement of GES/environmental targets by increasing the area of sea bottom where any kind of permanent anthropogenic change is banned. PL-D6-M032 will provide better understanding of the impacts of bottom trawling and thus will have an indirect positive impact in the form of more informed policymakiong and decisionmaking regarding bottom trawling. The combined measures aimed at reducing nutrient inputs will have a major, though indirect, impact on benthic communities. The species composition of these communities should begin to improve either directly due to reduced nutrient input (shallow zones) or due to reduction of oxygen deficit (deeper zones). Measures aimed at reducting nutrient inputs will have some positive impact also on the marine waters of neighbouring countries. The impact will be most visible with regard to D5 (Eutrophication) and less so with regard to D1/D4/D6 (Biodiversity/ Food webs/Bottom integrity). |
||
Measures ad hoc |
BALPL-M006 Establishment in marine spatial plans and in Natura 2000 protection plans of zones free from permanent human interference (measure continued from the first cycle, following major modifications);PL-D6-M032 Monitoring and limiting the scale of sea bottom and coast transformations (measure first introduced in the updated PoM) |
||
Further information |
https://chronmorze.eu/wp-content/uploads/2022/09/Projekt-aPOWM_23.08.2022.pdf
|
https://chronmorze.eu/wp-content/uploads/2022/09/Projekt-aPOWM_23.08.2022.pdf
|
https://chronmorze.eu/wp-content/uploads/2022/09/Projekt-aPOWM_23.08.2022.pdf
|