Member State report / Art8 / 2018 / D2 / Poland / Baltic Sea
Report type | Member State report to Commission |
MSFD Article | Art. 8 Initial assessment (and Art. 17 updates) |
Report due | 2018-10-15 |
GES Descriptor | D2 Non-indigenous species |
Member State | Poland |
Region/subregion | Baltic Sea |
Reported by | Chief Inspectorate of Environmental Protection |
Report date | 2020-01-28 |
Report access | ART8_GES_PL_kor_URL.xml |
Polish part of Opensea Bornholm Basin (L2-SEA-007-POL)
GES component |
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
---|---|---|---|---|---|---|---|
Feature |
Newly-introduced non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Element |
Not applicable |
Amphibalanus improvisus |
Cercopagis pengoi |
Gammarus tigrinus |
Marenzelleria spp. (neglecta & viridis) |
Mya arenaria |
Prorocentrum cordatum |
Element code |
Not applicable |
421139 |
234025 |
102296 |
129615 |
140430 |
232376 |
Element code source |
Link to other vocabulary or code lists that may be relevant
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Element 2 |
|||||||
Element 2 code |
|||||||
Element 2 code source |
|||||||
Element source |
National |
National |
National |
National |
National |
National |
|
Criterion |
D2C1
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
Parameter |
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Parameter other |
|||||||
Threshold value upper |
|||||||
Threshold value lower |
|||||||
Threshold qualitative |
|||||||
Threshold value source |
Helsinki Convention
|
||||||
Threshold value source other |
|||||||
Value achieved upper |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
|
Value achieved lower |
|||||||
Value unit |
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
Value unit other |
|||||||
Proportion threshold value |
100.0 |
||||||
Proportion value achieved |
100.0 |
||||||
Proportion threshold value unit |
% area of MRU achieving threshold value |
||||||
Trend |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
Yes |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description parameter |
|||||||
Related indicator |
|||||||
Criteria status |
Good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description criteria |
|||||||
Element status |
Good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description element |
|||||||
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
|||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
|||||||
GES extent threshold |
|||||||
GES extent achieved |
|||||||
GES extent unit |
Number of newly-introduced species |
||||||
GES achieved |
GES achieved |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
Description overall status |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter was 1. |
|
Assessments period |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
|
Polish part of Opensea Gdansk Basin (L2-SEA-008-POL)
GES component |
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Newly-introduced non-indigenous species
|
Newly-introduced non-indigenous species
|
Newly-introduced non-indigenous species
|
Newly-introduced non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Element |
Limnodrilus profundicola |
Melita nitida |
Palaemon macrodactylus |
Rangia cuneata |
Acartia (Acanthacartia) tonsa |
Alexandrium ostenfeldii |
Amphibalanus improvisus |
Cercopagis pengoi |
Dreissena polymorpha |
Marenzelleria spp. (neglecta & viridis) |
Mya arenaria |
Prorocentrum cordatum |
Rhithropanopeus harrisii |
Element code |
475838 |
146922 |
181372 |
156991 |
345943 |
109712 |
421139 |
234025 |
181566 |
129615 |
140430 |
232376 |
107414 |
Element code source |
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Element 2 |
|||||||||||||
Element 2 code |
|||||||||||||
Element 2 code source |
|||||||||||||
Element source |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
Criterion |
D2C1
|
D2C1
|
D2C1
|
D2C1
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
Parameter |
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Parameter other |
|||||||||||||
Threshold value upper |
|||||||||||||
Threshold value lower |
|||||||||||||
Threshold qualitative |
|||||||||||||
Threshold value source |
Helsinki Convention
|
Helsinki Convention
|
Helsinki Convention
|
Helsinki Convention
|
|||||||||
Threshold value source other |
|||||||||||||
Value achieved upper |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
Value achieved lower |
|||||||||||||
Value unit |
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
Value unit other |
|||||||||||||
Proportion threshold value |
|||||||||||||
Proportion value achieved |
|||||||||||||
Proportion threshold value unit |
% area of MRU achieving threshold value |
% area of MRU achieving threshold value |
% area of MRU achieving threshold value |
% area of MRU achieving threshold value |
|||||||||
Trend |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
No |
No |
No |
No |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description parameter |
|||||||||||||
Related indicator |
|||||||||||||
Criteria status |
Not good |
Not good |
Not good |
Not good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description criteria |
|||||||||||||
Element status |
Not good |
Not good |
Not good |
Not good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description element |
|||||||||||||
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
|||||||||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
|||||||||||||
GES extent threshold |
|||||||||||||
GES extent achieved |
4.00 |
4.00 |
4.00 |
4.00 |
|||||||||
GES extent unit |
Number of newly-introduced species |
Number of newly-introduced species |
Number of newly-introduced species |
Number of newly-introduced species |
|||||||||
GES achieved |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
Description overall status |
There were 4 newly introduced non indigenous species to Polish waters of Gdansk Basin. Not all of the species were non indigenous for the Baltic Sea. The species were: Limnodrilus profundicola, Melita nitida, Palaemon macrodactylus and Rangia cuneata. The last 2 species were found in the Vistula river mouth. |
There were 4 newly introduced non indigenous species to Polish waters of Gdansk Basin. Not all of the species were non indigenous for the Baltic Sea. The species were: Limnodrilus profundicola, Melita nitida, Palaemon macrodactylus and Rangia cuneata. The last 2 species were found in the Vistula river mouth. |
There were 4 newly introduced non indigenous species to Polish waters of Gdansk Basin. Not all of the species were non indigenous for the Baltic Sea. The species were: Limnodrilus profundicola, Melita nitida, Palaemon macrodactylus and Rangia cuneata. The last 2 species were found in the Vistula river mouth. |
There were 4 newly introduced non indigenous species to Polish waters of Gdansk Basin. Not all of the species were non indigenous for the Baltic Sea. The species were: Limnodrilus profundicola, Melita nitida, Palaemon macrodactylus and Rangia cuneata. The last 2 species were found in the Vistula river mouth. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter value was 3. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter value was 3. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter value was 3. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter value was 3. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter value was 3. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter value was 3. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter value was 3. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter value was 3. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter value was 3. |
Assessments period |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
|
|
|
|
|
|
|
Polish part of Opensea Eastern Gotland Basin (L2-SEA-009-POL)
GES component |
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
---|---|---|---|---|---|---|
Feature |
Newly-introduced non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Element |
Not applicable |
Amphibalanus improvisus |
Cercopagis pengoi |
Marenzelleria spp. (neglecta & viridis) |
Mya arenaria |
Prorocentrum cordatum |
Element code |
Not applicable |
421139 |
234025 |
129615 |
140430 |
232376 |
Element code source |
Link to other vocabulary or code lists that may be relevant
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Element 2 |
||||||
Element 2 code |
||||||
Element 2 code source |
||||||
Element source |
National |
National |
National |
National |
National |
|
Criterion |
D2C1
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
Parameter |
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Parameter other |
||||||
Threshold value upper |
||||||
Threshold value lower |
||||||
Threshold qualitative |
||||||
Threshold value source |
Helsinki Convention
|
|||||
Threshold value source other |
||||||
Value achieved upper |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
|
Value achieved lower |
||||||
Value unit |
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
Value unit other |
||||||
Proportion threshold value |
100.0 |
|||||
Proportion value achieved |
100.0 |
|||||
Proportion threshold value unit |
% area of MRU achieving threshold value |
|||||
Trend |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
Yes |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description parameter |
||||||
Related indicator |
||||||
Criteria status |
Good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description criteria |
||||||
Element status |
Good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description element |
||||||
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
||||||
GES extent threshold |
||||||
GES extent achieved |
||||||
GES extent unit |
Number of newly-introduced species |
|||||
GES achieved |
GES achieved |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
Description overall status |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter value was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter value was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter value was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter value was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter value was 1. |
|
Assessments period |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
|
|
|
|
|
Related targets |
|
|
|
|
|
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Bornholm Basin - PL TW I WB 8 very sheltered, fully mixed, substratum: silt/sandy silt/silty sand; ice cover >90 days, water rwesidence time 52 days (L4-POL-002)
GES component |
D2
|
D2
|
D2
|
D2
|
D2
|
D2
|
---|---|---|---|---|---|---|
Feature |
Newly-introduced non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Element |
Dreissena bugensis |
Amphibalanus improvisus |
Dreissena polymorpha |
Marenzelleria spp. (neglecta & viridis) |
Mya arenaria |
Potamopyrgus antipodarum |
Element code |
505319 |
421139 |
181566 |
129615 |
140430 |
147123 |
Element code source |
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Element 2 |
||||||
Element 2 code |
||||||
Element 2 code source |
||||||
Element source |
National |
National |
National |
National |
National |
National |
Criterion |
D2C1
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
D2C2
|
Parameter |
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Presence
|
Parameter other |
||||||
Threshold value upper |
||||||
Threshold value lower |
||||||
Threshold qualitative |
||||||
Threshold value source |
Helsinki Convention
|
|||||
Threshold value source other |
||||||
Value achieved upper |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
Value achieved lower |
||||||
Value unit |
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
(number of) species
|
Value unit other |
||||||
Proportion threshold value |
||||||
Proportion value achieved |
||||||
Proportion threshold value unit |
% area of MRU achieving threshold value |
|||||
Trend |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
No |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description parameter |
||||||
Related indicator |
||||||
Criteria status |
Not good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description criteria |
||||||
Element status |
Not good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description element |
||||||
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
||||||
GES extent threshold |
||||||
GES extent achieved |
1.00 |
|||||
GES extent unit |
Number of newly-introduced species |
|||||
GES achieved |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
GES expected to be achieved by 2020 |
Description overall status |
There was one newly introduced non indigenous species in Polish waters of Szczecin Lagoon: Dreissena bugensis. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter was 1. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status. Inventory-Parameter was 1. |
Assessments period |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
|
|
|
|
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Related targets |
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|
|
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|
|
Gdansk Basin - PL TW I WB 1 very sheltered, fully mixed, substratum: silt/sandy silt/silty sand; ice cover >90 days, water rwesidence time 52 days (L4-POL-003)
GES component |
D2
|
D2
|
D2
|
---|---|---|---|
Feature |
Newly-introduced non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Element |
Rangia cuneata |
Dreissena polymorpha |
Marenzelleria spp. (neglecta & viridis) |
Element code |
156991 |
181566 |
129615 |
Element code source |
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Element 2 |
|||
Element 2 code |
|||
Element 2 code source |
|||
Element source |
National |
National |
National |
Criterion |
D2C1
|
D2C2
|
D2C2
|
Parameter |
Presence
|
Presence
|
Presence
|
Parameter other |
|||
Threshold value upper |
|||
Threshold value lower |
|||
Threshold qualitative |
|||
Threshold value source |
Helsinki Convention
|
||
Threshold value source other |
|||
Value achieved upper |
1.0 |
1.0 |
1.0 |
Value achieved lower |
|||
Value unit |
(number of) species
|
(number of) species
|
(number of) species
|
Value unit other |
|||
Proportion threshold value |
|||
Proportion value achieved |
|||
Proportion threshold value unit |
% area of MRU achieving threshold value |
||
Trend |
Unknown |
Unknown |
Unknown |
Parameter achieved |
No |
Not assessed |
Not assessed |
Description parameter |
|||
Related indicator |
|||
Criteria status |
Not good |
Not assessed |
Not assessed |
Description criteria |
|||
Element status |
Not good |
Not assessed |
Not assessed |
Description element |
|||
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
|||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
|||
GES extent threshold |
|||
GES extent achieved |
1.00 |
||
GES extent unit |
Number of newly-introduced species |
||
GES achieved |
GES expected to be achieved by 2020 |
GES achieved |
GES achieved |
Description overall status |
There was one newly introduced non indigenous species in Polish waters of Vistula Lagoon: Rangia cuneata. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter was 0. |
The overall status is assessed based on all elements which are used to calculate the inventory parameter which focuses on changes in the number of established and new NIS detected in a specific assessment unit irrespective of regional species-baseline lists. The 'inventory' parameter quantifies whether the NIS species composition changes over time and focuses on changes in the total number of NIS individuals independent of the species list. The inventory is negative or zero if the number of NIS in assessment unit does not increase reflecting a good status.Inventory-Parameter was 0. |
Assessments period |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
|
|
Related targets |
|
|
|