Member State report / Art8 / 2018 / D1-B / 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 | D1 Birds |
| 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 marine waters (BAL-POL-MS-001)
GES component |
D1-B
|
D1-B
|
D1-B
|
|---|---|---|---|
Feature |
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Element |
Haliaeetus albicilla |
Haliaeetus albicilla |
Haliaeetus albicilla |
Element code |
232053 |
232053 |
232053 |
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 |
D1C3
|
D1C3
|
D1C3
|
Parameter |
Fecundity rate
|
Other
|
Other
|
Parameter other |
Brood size (climbed nests)
|
Productivity
|
|
Threshold value upper |
59.0 |
1.64 |
0.97 |
Threshold value lower |
|||
Threshold qualitative |
|||
Threshold value source |
National
|
National
|
National
|
Threshold value source other |
|||
Value achieved upper |
59.0 |
1.81 |
1.07 |
Value achieved lower |
|||
Value unit |
Other
|
Other
|
Other
|
Value unit other |
proportion
|
Mean number of nestlings
|
Mean number of nestlings
|
Proportion threshold value |
|||
Proportion value achieved |
|||
Proportion threshold value unit |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
Trend |
Unknown |
Unknown |
Unknown |
Parameter achieved |
Yes |
Yes |
Yes |
Description parameter |
Proportion of nests containing at least one nestling of at least three weeks of age, out of all occupied nests |
Mean number of nestlings of at least three weeks of age in nests containing young |
Mean number of nestlings of at least three weeks of age, out of all occupied nests |
Related indicator |
|||
Criteria status |
Good |
Good |
Good |
Description criteria |
In the years 2011-2016, all three analyzed parameters of white-tailed eagle reproduction were above the threshold value of a good state. |
In the years 2011-2016, all three analyzed parameters of white-tailed eagle reproduction were above the threshold value of a good state. |
In the years 2011-2016, all three analyzed parameters of white-tailed eagle reproduction were above the threshold value of a good state. |
Element status |
Good |
Good |
Good |
Description element |
In the years 2011-2016, all three analyzed parameters of white-tailed eagle reproduction were above the threshold value of a good state. |
In the years 2011-2016, all three analyzed parameters of white-tailed eagle reproduction were above the threshold value of a good state. |
In the years 2011-2016, all three analyzed parameters of white-tailed eagle reproduction were above the threshold value of a good state. |
Integration rule type parameter |
OOAO
|
OOAO
|
OOAO
|
Integration rule description parameter |
Good environmental status (GES) is assessed using 3 parameters of reproduction of the white-tailed eagles: breeding success, productivity and number of chicks. The assessment of the productivity of the white-tailed eagle is based on the principle: the result with the lowest rating determines the total score (OOAO) |
Good environmental status (GES) is assessed using 3 parameters of reproduction of the white-tailed eagles: breeding success, productivity and number of chicks. The assessment of the productivity of the white-tailed eagle is based on the principle: the result with the lowest rating determines the total score (OOAO) |
Good environmental status (GES) is assessed using 3 parameters of reproduction of the white-tailed eagles: breeding success, productivity and number of chicks. The assessment of the productivity of the white-tailed eagle is based on the principle: the result with the lowest rating determines the total score (OOAO) |
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
|||
GES extent threshold |
|||
GES extent achieved |
|||
GES extent unit |
|||
GES achieved |
GES achieved |
GES achieved |
GES achieved |
Description overall status |
|||
Assessments period |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
|
|
Related targets |
|
|
|
HELCOM designated MRU Borhnholm group for Polish avifauna assessment reporting (PL-SEA-L2-III-AVIFAUNA)
GES component |
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Benthic-feeding birds
|
Benthic-feeding birds
|
Benthic-feeding birds
|
Benthic-feeding birds
|
Benthic-feeding birds
|
Benthic-feeding birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Element |
Aythya ferina |
Aythya fuligula |
Aythya fuligula |
Aythya marila |
Bucephala clangula |
Somateria mollissima |
Anas acuta |
Anas penelope |
Anas platyrhynchos |
Anser anser |
Cygnus columbianus |
Cygnus cygnus |
Cygnus olor |
Cygnus olor |
Fulica atra |
Alca torda |
Mergellus albellus |
Mergus merganser |
Mergus merganser |
Mergus serrator |
Mergus serrator |
Phalacrocorax carbo |
Phalacrocorax carbo |
Podiceps cristatus |
Podiceps cristatus |
Uria aalge |
Hydroprogne caspia |
Larus argentatus |
Larus canus |
Larus fuscus |
Larus marinus |
Larus marinus |
Sterna hirundo |
Sterna paradisaea |
Sterna sandvicensis |
Sternula albifrons |
Anas crecca |
Calidris alpina |
Charadrius hiaticula |
Haematopus ostralegus |
Recurvirostra avosetta |
Tadorna tadorna |
Element code |
232037 |
159164 |
159164 |
159172 |
159197 |
137074 |
158939 |
159168 |
148791 |
416682 |
159088 |
159089 |
159090 |
159090 |
232054 |
137128 |
232039 |
159097 |
159097 |
159098 |
159098 |
137179 |
137179 |
137182 |
137182 |
137133 |
567825 |
137138 |
137141 |
137142 |
137146 |
137146 |
137162 |
137165 |
137166 |
567480 |
158943 |
159047 |
212619 |
147436 |
212721 |
232042 |
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/
|
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/
|
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/
|
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 |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
Criterion |
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
Parameter |
Abundance
|
Other
|
Other
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Other
|
Other
|
Abundance
|
Abundance
|
Abundance
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Other
|
Other
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Parameter other |
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
||||||||||||||||||||||||||||
Threshold value upper |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.8 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.8 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
Threshold value lower |
||||||||||||||||||||||||||||||||||||||||||
Threshold qualitative |
||||||||||||||||||||||||||||||||||||||||||
Threshold value source |
||||||||||||||||||||||||||||||||||||||||||
Threshold value source other |
||||||||||||||||||||||||||||||||||||||||||
Value achieved upper |
0.519 |
0.598 |
1.05 |
0.837 |
1.064 |
1.442 |
1.103 |
1.61 |
1.131 |
2.1 |
0.537 |
1.112 |
0.749 |
1.178 |
0.825 |
0.465 |
1.747 |
1.875 |
0.804 |
0.522 |
0.914 |
1.154 |
1.431 |
1.791 |
1.165 |
0.088 |
0.124 |
1.097 |
0.423 |
4.401 |
1.669 |
0.781 |
0.69 |
0.307 |
0.486 |
0.878 |
1.296 |
0.092 |
0.699 |
0.719 |
0.677 |
1.033 |
Value achieved lower |
||||||||||||||||||||||||||||||||||||||||||
Value unit |
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Value unit other |
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Proportion threshold value |
||||||||||||||||||||||||||||||||||||||||||
Proportion value achieved |
||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
||||||||||||||||||||||||||||||||||||||||||
Trend |
Deteriorating |
Deteriorating |
Stable |
Stable |
Improving |
Improving |
Unknown |
Improving |
Improving |
Improving |
Deteriorating |
Improving |
Deteriorating |
Improving |
Improving |
Unknown |
Improving |
Improving |
Deteriorating |
Deteriorating |
Stable |
Stable |
Improving |
Improving |
Improving |
Unknown |
Deteriorating |
Stable |
Deteriorating |
Improving |
Improving |
Unknown |
Deteriorating |
Deteriorating |
Unknown |
Stable |
Improving |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Stable |
Parameter achieved |
No |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
No |
Yes |
No |
Yes |
Yes |
Yes |
No |
No |
No |
Yes |
Yes |
No |
No |
Yes |
No |
Yes |
Description parameter |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Related indicator |
||||||||||||||||||||||||||||||||||||||||||
Criteria status |
Not good |
Not good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Not good |
Good |
Good |
Good |
Not good |
Not good |
Not good |
Good |
Good |
Not good |
Not good |
Good |
Not good |
Good |
Description criteria |
||||||||||||||||||||||||||||||||||||||||||
Element status |
Not good |
Not good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Not good |
Good |
Good |
Good |
Not good |
Not good |
Not good |
Good |
Good |
Not good |
Not good |
Good |
Not good |
Good |
Description element |
Wintering
|
Breeding and wintering
|
Breeding and wintering
|
Wintering
|
Wintering
|
Breeding
|
Wintering
|
Wintering
|
Wintering
|
Breeding
|
Wintering
|
Wintering
|
Breeding and wintering
|
Breeding and wintering
|
Wintering
|
Breeding
|
Wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Breeding and wintering
|
Breeding and wintering
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Wintering
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Integration rule type parameter |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description parameter |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
Integration rule type criteria |
||||||||||||||||||||||||||||||||||||||||||
Integration rule description criteria |
||||||||||||||||||||||||||||||||||||||||||
GES extent threshold |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
GES extent achieved |
0.60 |
0.60 |
0.60 |
0.60 |
0.60 |
0.60 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.57 |
0.57 |
0.57 |
0.57 |
0.57 |
0.57 |
0.57 |
0.57 |
0.57 |
0.57 |
0.57 |
0.44 |
0.44 |
0.44 |
0.44 |
0.44 |
0.44 |
0.44 |
0.44 |
0.44 |
0.44 |
0.50 |
0.50 |
0.50 |
0.50 |
0.50 |
0.50 |
GES extent unit |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
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 achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
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 |
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 |
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 |
||||||||||||||||||||||||||||||||||||||||||
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 |
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 |
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 |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
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Related targets |
|
|
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|
|
|
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|
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|
HELCOM designated MRU Gotland group for Polish avifauna assessment reporting (PL-SEA-L2-IV-AVIFAUNA)
GES component |
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Benthic-feeding birds
|
Benthic-feeding birds
|
Benthic-feeding birds
|
Benthic-feeding birds
|
Benthic-feeding birds
|
Benthic-feeding birds
|
Benthic-feeding birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Grazing birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Element |
Aythya ferina |
Aythya fuligula |
Aythya fuligula |
Aythya marila |
Bucephala clangula |
Melanitta fusca |
Somateria mollissima |
Anas platyrhynchos |
Anser anser |
Branta leucopsis |
Cygnus cygnus |
Cygnus olor |
Cygnus olor |
Fulica atra |
Alca torda |
Cepphus grylle |
Mergellus albellus |
Mergus merganser |
Mergus merganser |
Mergus serrator |
Mergus serrator |
Phalacrocorax carbo |
Phalacrocorax carbo |
Podiceps cristatus |
Podiceps cristatus |
Uria aalge |
Hydroprogne caspia |
Larus argentatus |
Larus argentatus |
Larus canus |
Larus canus |
Larus fuscus |
Larus marinus |
Larus marinus |
Larus ridibundus |
Sterna hirundo |
Sterna paradisaea |
Sternula albifrons |
Arenaria interpres |
Calidris alpina |
Charadrius hiaticula |
Haematopus ostralegus |
Recurvirostra avosetta |
Tadorna tadorna |
Element code |
232037 |
159164 |
159164 |
159172 |
159197 |
137072 |
137074 |
148791 |
416682 |
159177 |
159089 |
159090 |
159090 |
232054 |
137128 |
137130 |
232039 |
159097 |
159097 |
159098 |
159098 |
137179 |
137179 |
137182 |
137182 |
137133 |
567825 |
137138 |
137138 |
137141 |
137141 |
137142 |
137146 |
137146 |
137149 |
137162 |
137165 |
567480 |
147431 |
159047 |
212619 |
147436 |
212721 |
232042 |
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/
|
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/
|
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/
|
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 |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
HELCOM |
Criterion |
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
Parameter |
Abundance
|
Other
|
Other
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Other
|
Other
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Abundance
|
Abundance
|
Other
|
Other
|
Other
|
Other
|
Abundance
|
Other
|
Other
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Parameter other |
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
Abundance in breeding season
|
Abundance in wintering season
|
||||||||||||||||||||||||||
Threshold value upper |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.8 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.8 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
0.7 |
Threshold value lower |
||||||||||||||||||||||||||||||||||||||||||||
Threshold qualitative |
||||||||||||||||||||||||||||||||||||||||||||
Threshold value source |
||||||||||||||||||||||||||||||||||||||||||||
Threshold value source other |
||||||||||||||||||||||||||||||||||||||||||||
Value achieved upper |
0.295 |
1.438 |
1.083 |
1.279 |
1.867 |
0.495 |
0.131 |
1.778 |
0.843 |
0.315 |
2.199 |
1.834 |
1.132 |
0.431 |
2.442 |
0.284 |
3.437 |
0.852 |
0.919 |
1.309 |
1.075 |
2.05 |
1.791 |
3.067 |
1.869 |
2.306 |
1.186 |
0.351 |
1.124 |
1.049 |
0.674 |
0.141 |
0.273 |
0.727 |
4.945 |
3.298 |
2.62 |
1.242 |
0.31 |
0.093 |
1.285 |
0.964 |
0.523 |
0.498 |
Value achieved lower |
||||||||||||||||||||||||||||||||||||||||||||
Value unit |
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Value unit other |
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Population index value geometric mean
|
Proportion threshold value |
||||||||||||||||||||||||||||||||||||||||||||
Proportion value achieved |
||||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
||||||||||||||||||||||||||||||||||||||||||||
Trend |
Deteriorating |
Improving |
Improving |
Improving |
Improving |
Deteriorating |
Deteriorating |
Improving |
Improving |
Unknown |
Improving |
Deteriorating |
Improving |
Deteriorating |
Improving |
Improving |
Improving |
Deteriorating |
Deteriorating |
Stable |
Improving |
Stable |
Improving |
Improving |
Improving |
Improving |
Stable |
Stable |
Unknown |
Deteriorating |
Unknown |
Stable |
Deteriorating |
Unknown |
Unknown |
Improving |
Improving |
Stable |
Deteriorating |
Deteriorating |
Stable |
Improving |
Deteriorating |
Stable |
Parameter achieved |
No |
Yes |
Yes |
Yes |
Yes |
No |
No |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
No |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
No |
No |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
No |
Yes |
Yes |
No |
No |
Description parameter |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Trends observed in 1991-2016. Information from HELCOM indicator report. |
Related indicator |
||||||||||||||||||||||||||||||||||||||||||||
Criteria status |
Not good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Not good |
Good |
Good |
Good |
Not good |
Good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Not good |
Not good |
Description criteria |
||||||||||||||||||||||||||||||||||||||||||||
Element status |
Not good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Not good |
Good |
Good |
Good |
Not good |
Good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Not good |
Not good |
Description element |
Wintering
|
Breeding and wintering
|
Breeding and wintering
|
Wintering
|
Wintering
|
Breeding
|
Breeding
|
Wintering
|
Breeding
|
Breeding
|
Wintering
|
Breeding and wintering
|
Breeding and wintering
|
Wintering
|
Breeding
|
Breeding
|
Wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding
|
Breeding
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding and wintering
|
Breeding
|
Breeding and wintering
|
Breeding and wintering
|
Wintering
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Breeding
|
Integration rule type parameter |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description parameter |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
When a species abundance is assessed both in wintering and breeding season a OOAO principle is used e.g. the worst status of a given season determines the overall status of a species. |
Integration rule type criteria |
||||||||||||||||||||||||||||||||||||||||||||
Integration rule description criteria |
||||||||||||||||||||||||||||||||||||||||||||
GES extent threshold |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
0.75 |
GES extent achieved |
0.50 |
0.50 |
0.50 |
0.50 |
0.50 |
0.50 |
0.50 |
0.67 |
0.67 |
0.67 |
0.67 |
0.67 |
0.67 |
0.67 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.88 |
0.56 |
0.56 |
0.56 |
0.56 |
0.56 |
0.56 |
0.56 |
0.56 |
0.56 |
0.56 |
0.56 |
0.56 |
0.33 |
0.33 |
0.33 |
0.33 |
0.33 |
0.33 |
GES extent unit |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
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 |
GES expected to be achieved by 2020 |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
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 |
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 |
||||||||||||||||||||||||||||||||||||||||||||
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 |
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 |
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 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
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Related targets |
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