As part of EEA's ongoing security and identity management improvements, we are currently migrating the system to Entra ID authentication.
We kindly ask all users to start using Entra ID credentials when logging in to the system. 

Please note that LDAP authentication will be phased out and disabled by the end of August 2026. We encourage you to verify that you can successfully access the system and that your account and permissions function as expected after Entra ID login. Should you encounter any issues or require assistance during this transition, please contact Laszlo Cseh at laszlo.cseh@eaudeweb.ro Thank you for your cooperation and support.
As part of EEA's ongoing security and identity management improvements, we are currently migrating the system to Entra ID authentication.
We kindly ask all users to start using Entra ID credentials when logging in to the system. 

Please note that LDAP authentication will be phased out and disabled by the end of August 2026. We encourage you to verify that you can successfully access the system and that your account and permissions function as expected after Entra ID login. Should you encounter any issues or require assistance during this transition, please contact Laszlo Cseh at laszlo.cseh@eaudeweb.ro Thank you for your cooperation and support.

Member State report / Art10 / 2018 / D6 / Romania / Black Sea

Report type Member State report to Commission
MSFD Article Art. 10 Environmental targets (and Art. 17 updates)
Report due 2018-10-15
GES Descriptor D6 Sea-floor integrity/D1 Benthic habitats
Member State Romania
Region/subregion Black Sea
Reported by Ministerul Apelor si Padurilor
Report date 2020-04-06
Report access 3.msfd2018-ART10_Targets_18_12_03_05.xml

Target code
6.4
6.4
6.4
6.4
6.4
6.4
6.4
6.4
6.5.2
6.5.2
6.5.2
6.5.2
6.5.2
6.5.2
6.5.2
Target description
The extent of loss of each habitat type, resulting from anthropogenic pressures, does not exceed 5% of the natural extent of the habitat type in the marine unit.
The extent of loss of each habitat type, resulting from anthropogenic pressures, does not exceed 5% of the natural extent of the habitat type in the marine unit.
The extent of loss of each habitat type, resulting from anthropogenic pressures, does not exceed 5% of the natural extent of the habitat type in the marine unit.
The extent of loss of each habitat type, resulting from anthropogenic pressures, does not exceed 5% of the natural extent of the habitat type in the marine unit.
The extent of loss of each habitat type, resulting from anthropogenic pressures, does not exceed 5% of the natural extent of the habitat type in the marine unit.
The extent of loss of each habitat type, resulting from anthropogenic pressures, does not exceed 5% of the natural extent of the habitat type in the marine unit.
The extent of loss of each habitat type, resulting from anthropogenic pressures, does not exceed 5% of the natural extent of the habitat type in the marine unit.
The extent of loss of each habitat type, resulting from anthropogenic pressures, does not exceed 5% of the natural extent of the habitat type in the marine unit.
1. 75% of AMBI*(n) values > 0.68 in Mytilus galloprovincialis biogenic reefs on circalittoral mud, 2. 75% of AMBI*(n) values >0.61 in offshore circalittoral mud with Modiolula phaseolina, respectively
Average of EI>6 75% of M-AMBI*(n) values > 0.68 in infralittoral sand, circalittoral sand and circalittoral mud
75% of M-AMBI*(n) values > 0.61 in infralittoral sand and circalittoral mud
Average of EI>6 75% of M-AMBI*(n) values > 0.68 in infralittoral sand, circalittoral sand and circalittoral mud
Average of EI>6 75% of M-AMBI*(n) values > 0.68 in infralittoral sand, circalittoral sand and circalittoral mud
75% of M-AMBI*(n) values > 0.61 in infralittoral sand and circalittoral mud
1. 75% of AMBI*(n) values > 0.68 in Mytilus galloprovincialis biogenic reefs on circalittoral mud, 2. 75% of AMBI*(n) values >0.61 in offshore circalittoral mud with Modiolula phaseolina, respectively
Feature(s)
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
  • Benthic habitats
GES components
  • D6C4 Benthic habitat extent (1.4, 1.4.1, 1.4.2, 1.5, 1.5.1, 6.1.1)
  • D6C4 Benthic habitat extent (1.4, 1.4.1, 1.4.2, 1.5, 1.5.1, 6.1.1)
  • D6C4 Benthic habitat extent (1.4, 1.4.1, 1.4.2, 1.5, 1.5.1, 6.1.1)
  • D6C4 Benthic habitat extent (1.4, 1.4.1, 1.4.2, 1.5, 1.5.1, 6.1.1)
  • D6C4 Benthic habitat extent (1.4, 1.4.1, 1.4.2, 1.5, 1.5.1, 6.1.1)
  • D6C4 Benthic habitat extent (1.4, 1.4.1, 1.4.2, 1.5, 1.5.1, 6.1.1)
  • D6C4 Benthic habitat extent (1.4, 1.4.1, 1.4.2, 1.5, 1.5.1, 6.1.1)
  • D6C4 Benthic habitat extent (1.4, 1.4.1, 1.4.2, 1.5, 1.5.1, 6.1.1)
  • D6C5 Benthic habitat condition (1.6, 1.6.1, 1.6.2, 1.6.3, 6.2, 6.2.1, 6.2.2, 6.2.3, 6.2.4)
  • D6C5 Benthic habitat condition (1.6, 1.6.1, 1.6.2, 1.6.3, 6.2, 6.2.1, 6.2.2, 6.2.3, 6.2.4)
  • D6C5 Benthic habitat condition (1.6, 1.6.1, 1.6.2, 1.6.3, 6.2, 6.2.1, 6.2.2, 6.2.3, 6.2.4)
  • D6C5 Benthic habitat condition (1.6, 1.6.1, 1.6.2, 1.6.3, 6.2, 6.2.1, 6.2.2, 6.2.3, 6.2.4)
  • D6C5 Benthic habitat condition (1.6, 1.6.1, 1.6.2, 1.6.3, 6.2, 6.2.1, 6.2.2, 6.2.3, 6.2.4)
  • D6C5 Benthic habitat condition (1.6, 1.6.1, 1.6.2, 1.6.3, 6.2, 6.2.1, 6.2.2, 6.2.3, 6.2.4)
  • D6C5 Benthic habitat condition (1.6, 1.6.1, 1.6.2, 1.6.3, 6.2, 6.2.1, 6.2.2, 6.2.3, 6.2.4)
Timescale
202012
202012
202012
202012
202012
202012
202012
202012
202012
202012
202012
202012
202012
202012
202012
Update date
201812
201812
201812
201812
201812
201812
201812
201812
201407
201407
201407
201407
201407
201407
201407
Update type
New target
New target
New target
New target
New target
New target
New target
New target
Modified from 2012 definition
Modified from 2012 definition
Modified from 2012 definition
Modified from 2012 definition
Modified from 2012 definition
Modified from 2012 definition
Modified from 2012 definition
Marine reporting unit
  • BLK_RO_RG_CT
  • BLK_RO_RG_TT03
  • BLK_RO_RG_MT01
  • BLK_RO_RG_CT
  • BLK_RO_RG_TT03
  • BLK_RO_RG_TT03
  • BLK_RO_RG_CT
  • BLK_RO_RG_TT03
  • BLK_RO_RG_MT01
  • BLK_RO_RG_MT01
  • BLK_RO_RG_CT
  • BLK_RO_RG_TT03
  • BLK_RO_RG_CT
  • BLK_RO_RG_CT
  • BLK_RO_RG_TT03
  • BLK_RO_RG_MT01
Element
Circalittoral mud
Circalittoral mud
Circalittoral sand
Circalittoral sand
Infralittoral mud
Infralittoral sand
Infralittoral sand
Offshore circalittoral mud
Biogenic reefs on circalittoral mud
Circalittoral mud
Circalittoral mud
Circalittoral sand
Infralittoral sand
Infralittoral sand
Offshore circalittoral mud
Element 2
Mytillus galoprovincialis
Modiolula phaseolina
Parameter
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Habitat condition
Habitat condition
Habitat condition
Habitat condition
Habitat condition
Habitat condition
Habitat condition
Parameter - other
Target value
5.0
5.0
5.0
5.0
5.0
5.0
5.0
5.0
0.68
0.68
0.61
0.68
0.68
0.61
0.61
Value achieved - upper
0.05
0.89
1.2
0.08
0.98
0.95
0.99
1.014
0.92
1.0
1.0
Value achieved - lower
0.23
0.65
0.53
0.4
0.61
0.53
0.71
Value unit
percentage
percentage
percentage
percentage
percentage
percentage
percentage
percentage
Other
Other
Other
Other
Value unit - other
M-AMBI(n)
M-AMBI(n)
M-AMBI(n)
M-AMBI(n)
Target status
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target not yet achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Assessment period
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
Target assessment description
Related indicator
  • 6.4
  • 6.4
  • 6.4
  • 6.4
  • 6.4
  • 6.4
  • 6.4
  • 6.4
  • 6.5.2
  • 6.5.2
  • 6.5.2
  • 6.5.2
  • 6.5.2
  • 6.5.2
  • 6.5.2
Related measures
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036
  • BLKRO-M001
  • BLKRO-M003
  • BLKRO-M007
  • BLKRO-M032
  • BLKRO-M035
  • BLKRO-M036