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
GES descriptor, criterion or indicator [GEScomponent]
D6
D6C4
D6C4
D1C6
D1C6
D6C4
D6C3
D6C5
D6C5
MarineUnitID
  • Baltic Sea (BAL-FI-RG-Baltic_Sea)
  • Baltic Sea (BAL-FI-RG-Baltic_Sea)
  • Baltic Sea (BAL-FI-RG-Baltic_Sea)
  • Baltic Sea (BAL-FI-RG-Baltic_Sea)
  • Baltic Sea (BAL-FI-RG-Baltic_Sea)
  • Baltic Sea (BAL-FI-RG-Baltic_Sea)
  • Baltic Sea (BAL-FI-RG-Baltic_Sea)
  • Baltic Sea (BAL-FI-RG-Baltic_Sea)
  • Baltic Sea (BAL-FI-RG-Baltic_Sea)
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.
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.
Habitat Distribution Area in Finnish Sea Areas, using the EUNIS classification of habitats, under development by HELCOM
Habitat Areas in Finnish Sea Areas, using the EUNIS classification of habitats, under development by HELCOM
Status of species and communities typical of habitats
Occurrence and abundance of juvenile whitefish and flounder on shallow sandy bottoms
Number of environmental permits granted and number of dredging spoils included
Cumulative effect of human activity
BBI Index for the diversity and sensitivity of coastal communities
Index of the geological stability (physical integrity) of the seabed
Threshold value [TargetValue]
Reference point type
Baseline
Proportion
Assessment method
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
Timescale
Interim or GES target
Compatibility with existing targets/indicators
Physical/chemical features
Predominant habitats
  • SeabedHabitatsAll
  • SeabedHabitatsAll
  • SeabedHabitatsAll
  • SeabedHabitatsAll
Functional group
Pressures
  • PhysDam
  • PhysDam
  • PhysDam
  • PhysDam
  • PhysDam