Member State report / Art10 / 2012 / D6 / Finland / Baltic Sea
Report type | Member State report to Commission |
MSFD Article | Art. 10 Environmental targets (and Art. 17 updates) |
Report due | 2012-10-15 |
GES Descriptor | D6 Sea-floor integrity/D1 Benthic habitats |
Member State | Finland |
Region/subregion | Baltic Sea |
Reported by | Team of experts from: - several Finnish Institutes, - Centres for Economic Development, Transport and the Environment - The Ministry of Enviroment |
Report date | 2012-11-09 |
Report access | MSFD10TI_20130515_140728.xml |
BAL-FI-RG-Baltic_Sea
Feature [Target or Indicator code] |
D6 |
1.4.1 |
1.5.1 |
1.6.1 |
1.6.2 |
6.1.1 |
6.1.2 |
6.2.1 |
6.2.2 |
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GES descriptor, criterion or indicator [GEScomponent] |
D6
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D6C4
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D6C4
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D1C6
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D1C6
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D6C4
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D6C3
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D6C5
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D6C5
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MarineUnitID |
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Method used |
Good status is defined qualitatively for each of the evaluation criteria and qualitative targets are also set for each criterion. A good status limit (s), which can be either quantitative or qualitative, is set for hot indicators, unless quantitative values can be scientifically set.
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Good status is defined qualitatively for each of the evaluation criteria and qualitative targets are also set for each criterion. A good status limit (s), which can be either quantitative or qualitative, is set for hot indicators, unless quantitative values can be scientifically set.
|
Good status is defined qualitatively for each of the evaluation criteria and qualitative targets are also set for each criterion. A good status limit (s), which can be either quantitative or qualitative, is set for hot indicators, unless quantitative values can be scientifically set.
|
Good status is defined qualitatively for each of the evaluation criteria and qualitative targets are also set for each criterion. A good status limit (s), which can be either quantitative or qualitative, is set for hot indicators, unless quantitative values can be scientifically set.
|
Good status is defined qualitatively for each of the evaluation criteria and qualitative targets are also set for each criterion. A good status limit (s), which can be either quantitative or qualitative, is set for hot indicators, unless quantitative values can be scientifically set.
|
Good status is defined qualitatively for each of the evaluation criteria and qualitative targets are also set for each criterion. A good status limit (s), which can be either quantitative or qualitative, is set for hot indicators, unless quantitative values can be scientifically set.
|
Good status is defined qualitatively for each of the evaluation criteria and qualitative targets are also set for each criterion. A good status limit (s), which can be either quantitative or qualitative, is set for hot indicators, unless quantitative values can be scientifically set.
|
Good status is defined qualitatively for each of the evaluation criteria and qualitative targets are also set for each criterion. A good status limit (s), which can be either quantitative or qualitative, is set for hot indicators, unless quantitative values can be scientifically set.
|
Good status is defined qualitatively for each of the evaluation criteria and qualitative targets are also set for each criterion. A good status limit (s), which can be either quantitative or qualitative, is set for hot indicators, unless quantitative values can be scientifically set.
|
Description [Targets] |
Anthropogenic pressures on the seabed are local and the cumulative effects of these pressures do not interfere with the natural structure and function of the benthic ecosystems.
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Habitat Distribution Area in Finnish Sea Areas, using the EUNIS classification of habitats, under development by HELCOM
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Habitat Areas in Finnish Sea Areas, using the EUNIS classification of habitats, under development by HELCOM
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Status of species and communities typical of habitats
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Occurrence and abundance of juvenile whitefish and flounder on shallow sandy bottoms
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Number of environmental permits granted and number of dredging spoils included
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Cumulative effect of human activity
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BBI Index for the diversity and sensitivity of coastal communities
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Index of the geological stability (physical integrity) of the seabed
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Threshold value [TargetValue] |
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Reference point type |
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Baseline |
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Proportion |
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Assessment method |
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Development status |
operational by 2014 |
operational by 2018 |
operational by 2018 |
operational by 2018 |
operational by 2018 |
operational by 2014 |
operational by 2014 |
operational by 2014 |
operational by 2014 |
Type of target/indicator |
Pressure |
Pressure |
Pressure |
State |
State |
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Timescale |
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Interim or GES target |
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Compatibility with existing targets/indicators |
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Physical/chemical features |
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Predominant habitats |
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Functional group |
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Pressures |
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