Member State report: Germany / Art3-4

Report type Member State report to Commission
MSFD Article Art. 3(1) Marine waters & Art. 4/2017 Decision: Marine regions, subregions, and subdivisions & Art. 5(2) & Art. 6 Regional cooperation
Member State Germany
Reported by Bundesministerium fuer Umwelt, Naturschutz und nukleare Sicherheit
Report date 2019-08-27
Report access BALDE_MSFD4Geo_20190827.xml
Member state marine waters
The German marine waters including the seabed and subsoil relate to the German part of the North Sea and Baltic sea. The outer limit of the area are identical with the Exclusive Economic Zone (EEZ).
Region / subregion description
The German Subregion ANSDE and BALDE cover the German part of the North Sea and the Baltic Sea.
Subdivisions
Germany defined for the 2018 reporting new assessment scales on selected GES criteria. For these criteria the following area types have been choosen: Territorial waters as defined under the WFD, Coastal waters as defined under the WFD, Fishing area, MS marine waters part of a Region or Subregion. Because of the fact that these area types are not part of the area type codelist of the MSFD4geo schema Germany mapped them to 'SD_Subdivision' and 'MS_PartRegionSubregion'.
MRUs description (AreaType)
No formal assessment areas have been defined.
MRUs
Region or subregion Member state Area type Marine Reporting Unit MRU Name
BAL DE SD_Subdivision BALDE_CW
BALDE_CW
BAL DE SD_Subdivision BALDE_CW_AB
BALDE_CW_AB
BAL DE SD_Subdivision BALDE_CW_BB
BALDE_CW_BB
BAL DE SD_Subdivision BALDE_CW_D5_AB_B2
BALDE_CW_D5_AB_B2
BAL DE SD_Subdivision BALDE_CW_D5_AB_B3
BALDE_CW_D5_AB_B3
BAL DE SD_Subdivision BALDE_CW_D5_BB_B2
BALDE_CW_D5_BB_B2
BAL DE SD_Subdivision BALDE_CW_D5_BB_B3
BALDE_CW_D5_BB_B3
BAL DE SD_Subdivision BALDE_CW_D5_GB_B3
BALDE_CW_D5_GB_B3
BAL DE SD_Subdivision BALDE_CW_D5_KB_B2
BALDE_CW_D5_KB_B2
BAL DE SD_Subdivision BALDE_CW_D5_KB_B3
BALDE_CW_D5_KB_B3
BAL DE SD_Subdivision BALDE_CW_D5_MB_B2
BALDE_CW_D5_MB_B2
BAL DE SD_Subdivision BALDE_CW_D5_MB_B3
BALDE_CW_D5_MB_B3
BAL DE SD_Subdivision BALDE_CW_KB
BALDE_CW_KB
BAL DE SD_Subdivision BALDE_CW_MB
BALDE_CW_MB
BAL DE SD_Subdivision BALDE_EEZ
BALDE_EEZ
BAL DE SD_Subdivision BALDE_EEZ_AB
BALDE_EEZ_AB
BAL DE SD_Subdivision BALDE_EEZ_BB
BALDE_EEZ_BB
BAL DE SD_Subdivision BALDE_EEZ_KB
BALDE_EEZ_KB
BAL DE SD_Subdivision BALDE_EEZ_MB
BALDE_EEZ_MB
BAL DE SD_Subdivision BALDE_FA_3c22
BALDE_FA_3c22
BAL DE SD_Subdivision BALDE_FA_3d24
BALDE_FA_3d24
BAL DE MS_MarineWatersPartRegionSubregion BALDE_MS
BALDE_MS
BAL DE SD_Subdivision BALDE_OFFSHORE_AB
BALDE_OFFSHORE_AB
BAL DE SD_Subdivision BALDE_OFFSHORE_BB
BALDE_OFFSHORE_BB
BAL DE SD_Subdivision BALDE_OFFSHORE_KB
BALDE_OFFSHORE_KB
BAL DE SD_Subdivision BALDE_OFFSHORE_MB
BALDE_OFFSHORE_MB
BAL DE SD_Subdivision DE_CW_B0.9610
DE_CW_B0.9610
BAL DE SD_Subdivision DE_CW_B2.9610.07.01
DE_CW_B2.9610.07.01
BAL DE SD_Subdivision DE_CW_B2.9610.07.02
DE_CW_B2.9610.07.02
BAL DE SD_Subdivision DE_CW_B2.9610.07.03
DE_CW_B2.9610.07.03
BAL DE SD_Subdivision DE_CW_B2.9610.07.04
DE_CW_B2.9610.07.04
BAL DE SD_Subdivision DE_CW_B2.9610.09.01
DE_CW_B2.9610.09.01
BAL DE SD_Subdivision DE_CW_B2.9610.09.02
DE_CW_B2.9610.09.02
BAL DE SD_Subdivision DE_CW_B2.9610.10.01
DE_CW_B2.9610.10.01
BAL DE SD_Subdivision DE_CW_B2.9610.10.02
DE_CW_B2.9610.10.02
BAL DE SD_Subdivision DE_CW_B2.9610.10.03
DE_CW_B2.9610.10.03
BAL DE SD_Subdivision DE_CW_B3.9610.07.05
DE_CW_B3.9610.07.05
BAL DE SD_Subdivision DE_CW_B3.9610.07.06
DE_CW_B3.9610.07.06
BAL DE SD_Subdivision DE_CW_B3.9610.07.07
DE_CW_B3.9610.07.07
BAL DE SD_Subdivision DE_CW_B3.9610.09.03
DE_CW_B3.9610.09.03
BAL DE SD_Subdivision DE_CW_B3.9610.09.04
DE_CW_B3.9610.09.04
BAL DE SD_Subdivision DE_CW_B3.9610.09.05
DE_CW_B3.9610.09.05
BAL DE SD_Subdivision DE_CW_B3.9610.09.06
DE_CW_B3.9610.09.06
BAL DE SD_Subdivision DE_CW_B3.9610.09.07
DE_CW_B3.9610.09.07
BAL DE SD_Subdivision DE_CW_B3.9610.09.08
DE_CW_B3.9610.09.08
BAL DE SD_Subdivision DE_CW_B3.9610.09.09
DE_CW_B3.9610.09.09
BAL DE SD_Subdivision DE_CW_B4.9610.07.08
DE_CW_B4.9610.07.08
BAL DE SD_Subdivision DE_CW_B4.9610.07.09
DE_CW_B4.9610.07.09
BAL DE SD_Subdivision DE_CW_B4.9610.09.10
DE_CW_B4.9610.09.10
BAL DE SD_Subdivision DE_CW_B4.9610.09.11
DE_CW_B4.9610.09.11
BAL DE SD_Subdivision DE_CW_B4.9610.09.12
DE_CW_B4.9610.09.12
BAL DE SD_Subdivision DE_CW_DEMV_OD_01
DE_CW_DEMV_OD_01
BAL DE SD_Subdivision DE_CW_DEMV_WP_01
DE_CW_DEMV_WP_01
BAL DE SD_Subdivision DE_CW_DEMV_WP_02
DE_CW_DEMV_WP_02
BAL DE SD_Subdivision DE_CW_DEMV_WP_03
DE_CW_DEMV_WP_03
BAL DE SD_Subdivision DE_CW_DEMV_WP_04
DE_CW_DEMV_WP_04
BAL DE SD_Subdivision DE_CW_DEMV_WP_05
DE_CW_DEMV_WP_05
BAL DE SD_Subdivision DE_CW_DEMV_WP_06
DE_CW_DEMV_WP_06
BAL DE SD_Subdivision DE_CW_DEMV_WP_07
DE_CW_DEMV_WP_07
BAL DE SD_Subdivision DE_CW_DEMV_WP_08
DE_CW_DEMV_WP_08
BAL DE SD_Subdivision DE_CW_DEMV_WP_09
DE_CW_DEMV_WP_09
BAL DE SD_Subdivision DE_CW_DEMV_WP_10
DE_CW_DEMV_WP_10
BAL DE SD_Subdivision DE_CW_DEMV_WP_11
DE_CW_DEMV_WP_11
BAL DE SD_Subdivision DE_CW_DEMV_WP_12
DE_CW_DEMV_WP_12
BAL DE SD_Subdivision DE_CW_DEMV_WP_13
DE_CW_DEMV_WP_13
BAL DE SD_Subdivision DE_CW_DEMV_WP_14
DE_CW_DEMV_WP_14
BAL DE SD_Subdivision DE_CW_DEMV_WP_15
DE_CW_DEMV_WP_15
BAL DE SD_Subdivision DE_CW_DEMV_WP_16
DE_CW_DEMV_WP_16
BAL DE SD_Subdivision DE_CW_DEMV_WP_17
DE_CW_DEMV_WP_17
BAL DE SD_Subdivision DE_CW_DEMV_WP_18
DE_CW_DEMV_WP_18
BAL DE SD_Subdivision DE_CW_DEMV_WP_19
DE_CW_DEMV_WP_19
BAL DE SD_Subdivision DE_CW_DEMV_WP_20
DE_CW_DEMV_WP_20
BAL DE SD_Subdivision DE_CW_DEMV_WP_21
DE_CW_DEMV_WP_21
Region/ subregion
BAL
Art. 8 countries involved
EE, DE, PL, LT, FI, DK, SE, RU, LV, ,
Art. 8 nature of coordination
1. There has been a high level of information sharing, joint assessment and agreed methodologies in the Baltic Sea region through HELCOM work with broad participation of experts in the many HELCOM groups. The development of the set of HELCOM core indicators has been a focus of regional cooperation. 2. The HELCOM State of the Baltic Sea report (SoBS, http://stateofthebalticsea.helcom.fi/) is the regionally coherent contribution to national initial assessments of EU Member States in the Baltic Sea. 3. The SoBS report refers to defined spatial units representing varying levels of detail, in a regionally agreed nested system. Trends are shown mainly at regional scale and as large-scale patterns between geographic areas. 4. The SoBS report summarises the holistic assessment of the environmental status of the Baltic Sea for the period 2011-2016. Trends indicate potential future developments and geographic areas of key importance for the assessed themes. The report builds on common HELCOM indicators, thematic assessments, supporting material and spatial data fact sheets. 5. In the SoBS report, thirty core indicators assess the status of selected elements of biodiversity and human-induced pressures, based on current knowledge and available data, mostly from coordinated HELCOM monitoring programmes. Six indicators and/or their associated HELCOM threshold value used in the SoBS report are still being tested in some countries and may be further developed in HELCOM as a result of the outcome of the testing. In some cases the results may show that the indicator is not suitable for use in a specific sub-basin. These indicators should be therefore considered as intermediate. Some countries have used them as a basis for national indicators. 6. In the SoBS report, tthematic assessments for biodiversity, eutrophication and contaminants integrate indicator results at regional scale. The assessment of marine litter, underwater sound and seabed loss and disturbance is descriptive as HELCOM core indicators are still under development. 7. In the SoBS report, thirty-six ecosystem layers and eighteen aggregated pressure layers feed into the further developed Baltic Sea Pressure and Impact Indexes. They depict, based on best available regional data, the spatial distribution of cumulative pressures and potential cumulative impacts on ecosystem components in the Baltic Sea. 8. In the SoBS report, results from the economic and social analysis are included for themes where information at the regional scale is available. 9. All material is available online, including for EU reporting purposes. This includes indicator reports as well as data and information resulting from- and underpinning - the assessments. 10. There remain still gaps in harmonized valuation methods and indicator threshold values. Therefore the national Initial Assessments are not always comparable. However no country has flagged major inconsistencies in the conclusions of neighbouring national initial assessments.
Art. 8 regional coherence
Partial
Art. 8 regional coherence problems
Art. 9 countries involved
EE, DE, PL, LT, FI, DK, SE, RU, LV, ,
Art. 9 nature of coordination
1. There has been a moderate level of information sharing in the development of coherent good environmental status (GES) determinations at descriptor and criteria level through HELCOM. 2. HELCOM work supports the cooperation between EU Member States towards coherent and measurable determinations of GES based on the best available evidence. The HELCOM Working Group on Implementing the Ecosystem Approach (GEAR) works to identify opportunities for (sub)regionally coherent GES determinations and common GES determinations. In 2018/2019 GEAR will consider how to take forward future information exchange on national GES determinations. 3. There has been a high level of cooperation and progress in HELCOM work on developing common indicators. 4. At this point in time, HOLAS II indicators and threshold values should not automatically be considered as equivalent to criteria threshold values in the sense of Commission Decision (EU) 2017/848 laying down criteria and methodological standards on good environmental status, but can be used for the purposes of their Marine Strategy Framework Directive obligations by those Contracting Parties being EU Member States that wish to do so. 5. In 2018, HELCOM agreed to undertake an analysis to identify where coherent definitions of threshold values, lists of elements and integration methods are needed and agree concrete steps to this end. In 2018 HELCOM also agreed a work plan to progress the work on HELCOM indicators which includes an analysis of adjustment needs and gaps in order to support future ecosystem assessments that can contribute to the assessment of the extent to which GES has been achieved under MSFD.
Art. 9 regional coherence
Partial
Art. 9 regional coherence problems
After the adoption of the GES Commission Decision there was no time left for EU Member States to exchange information and jointly work on the ultimate GES determinations (to which indicators and integrated assessment methods contribute) for reporting in 2018. There is political hesitation regarding setting coordinated, quantified GES-determinations under Art. 9 MSFD.
Art. 10 countries involved
EE, DE, PL, LT, FI, DK, SE, RU, LV, ,
Art. 10 nature of coordination
1. There has been a moderate level of information sharing on the development of coordinated environmental targets and indicators. 2. EU Member States aim to work together with other countries through HELCOM to contribute to strengthening regional coordination in the implementation of the MSFD and to ensuring coherence with regard to the establishment of environmental targets. 3. HELCOM has set Maximum Allowable Inputs and country-allocated reduction targets for nutrients in 2007, updated them in 2013 and followed them up since then, in order to lower nutrient inputs and to combat human-made eutrophication. 4. In 2016/2017, the EU-funded project Baltic BOOST supported HELCOM cooperation in exploring initial methods on how the development of environmental targets relating to underwater noise and seafloor integrity could be approached in the future. In 2018, HELCOM Ministers committed to developing regionally coordinated, quantitative targets to reduce input of litter, physical disturbance caused by human activities and habitat loss. They also committed to develop an action plan, preferably by 2021, and regionally coordinated actions on underwater noise. 5. In 2018/2019 GEAR will share information on national targets and develop a way forward towards enhancing cooperation on defining coherent environmental targets.
Art. 10 regional coherence
Partial
Art. 10 regional coherence problems
Progress has been hampered by limited knowledge. There is also currently a lack of consensus on methodologies and/or political back up for setting further specific coordinated quantified targets. In spring 2018 there was a political decision to develop regionally coordinated, quantitative targets to reduce input of litter; and to develop the necessary regionally coordinated quantitative targets for the reduction of physical disturbance caused by human activities and habitat loss, however work on this has yet to commence.

Report type Member State report to Commission
MSFD Article Art. 3(1) Marine waters & Art. 4/2017 Decision: Marine regions, subregions, and subdivisions & Art. 5(2) & Art. 6 Regional cooperation
Member State Germany
Reported by Bundesministerium fuer Umwelt, Naturschutz und nukleare Sicherheit
Report date 2019-08-27
Report access ANSDE_MSFD4Geo_20190827.xml
Member state marine waters
The German marine waters including the seabed and subsoil relate to the German part of the North Sea and Baltic sea. The outer limit of the area are identical with the Exclusive Economic Zone (EEZ).
Region / subregion description
The German Subregion ANSDE and BALDE cover the German part of the North Sea and the Baltic Sea.
Subdivisions
Germany defined for the 2018 reporting new assessment scales on selected GES criteria. For these criteria the following area types have been choosen: Territorial waters as defined under the WFD, Coastal waters as defined under the WFD, Fishing area, MS marine waters part of a Region or Subregion. Because of the fact that these area types are not part of the area type codelist of the MSFD4geo schema Germany mapped them to 'SD_Subdivision' and 'MS_PartRegionSubregion'.
MRUs description (AreaType)
No formal assessment areas have been defined.
MRUs
Region or subregion Member state Area type Marine Reporting Unit MRU Name
ANS DE SD_Subdivision ANSDE_BRG
ANSDE_BRG
ANS DE SD_Subdivision ANSDE_CW
ANSDE_CW
ANS DE SD_Subdivision ANSDE_D5_EF12
ANSDE_D5_EF12
ANS DE SD_Subdivision ANSDE_D5_EF34
ANSDE_D5_EF34
ANS DE SD_Subdivision ANSDE_D5_EW34
ANSDE_D5_EW34
ANS DE SD_Subdivision ANSDE_D5_ICEF
ANSDE_D5_ICEF
ANS DE SD_Subdivision ANSDE_D5_ICNF
ANSDE_D5_ICNF
ANS DE SD_Subdivision ANSDE_D5_NF12
ANSDE_D5_NF12
ANS DE SD_Subdivision ANSDE_D5_OCEF
ANSDE_D5_OCEF
ANS DE SD_Subdivision ANSDE_D5_OCNF
ANSDE_D5_OCNF
ANS DE SD_Subdivision ANSDE_D5_OFFI
ANSDE_D5_OFFI
ANS DE SD_Subdivision ANSDE_D5_OFFO
ANSDE_D5_OFFO
ANS DE SD_Subdivision ANSDE_DBN
ANSDE_DBN
ANS DE SD_Subdivision ANSDE_DBS
ANSDE_DBS
ANS DE SD_Subdivision ANSDE_EEZ
ANSDE_EEZ
ANS DE SD_Subdivision ANSDE_EUT
ANSDE_EUT
ANS DE MS_MarineWatersPartRegionSubregion ANSDE_MS
ANSDE_MS
ANS DE SD_Subdivision ANSDE_ODB
ANSDE_ODB
ANS DE SD_Subdivision ANSDE_TeW
ANSDE_TeW
ANS DE SD_Subdivision ANSDE_offshore
ANSDE_offshore
ANS DE SD_Subdivision DE_CW_N0.3900
DE_CW_N0.3900
ANS DE SD_Subdivision DE_CW_N0.3990
DE_CW_N0.3990
ANS DE SD_Subdivision DE_CW_N0.4000
DE_CW_N0.4000
ANS DE SD_Subdivision DE_CW_N0.5000
DE_CW_N0.5000
ANS DE SD_Subdivision DE_CW_N0.9500
DE_CW_N0.9500
ANS DE SD_Subdivision DE_CW_N1.9500.01.01
DE_CW_N1.9500.01.01
ANS DE SD_Subdivision DE_CW_N1.9500.01.02
DE_CW_N1.9500.01.02
ANS DE SD_Subdivision DE_CW_N1_3100_01
EN_CW_N1_3100_01
ANS DE SD_Subdivision DE_CW_N1_4900_01
EN_CW_N1_4900_01
ANS DE SD_Subdivision DE_CW_N2.9500.01.03
DE_CW_N2.9500.01.03
ANS DE SD_Subdivision DE_CW_N2.9500.01.04
DE_CW_N2.9500.01.04
ANS DE SD_Subdivision DE_CW_N2.9500.01.05
DE_CW_N2.9500.01.05
ANS DE SD_Subdivision DE_CW_N2.9500.01.06
DE_CW_N2.9500.01.06
ANS DE SD_Subdivision DE_CW_N2_3100_01
EN_CW_N2_3100_01
ANS DE SD_Subdivision DE_CW_N2_4900_01
EN_CW_N2_4900_01
ANS DE SD_Subdivision DE_CW_N3.5000.04.01
DE_CW_N3.5000.04.01
ANS DE SD_Subdivision DE_CW_N3.9500.02.01
DE_CW_N3.9500.02.01
ANS DE SD_Subdivision DE_CW_N3.9500.03.01
DE_CW_N3.9500.03.01
ANS DE SD_Subdivision DE_CW_N3_3990_01
EN_CW_N3_3990_01
ANS DE SD_Subdivision DE_CW_N3_4900_01
EN_CW_N3_4900_01
ANS DE SD_Subdivision DE_CW_N4.5000.04.02
DE_CW_N4.5000.04.02
ANS DE SD_Subdivision DE_CW_N4.9500.02.02
DE_CW_N4.9500.02.02
ANS DE SD_Subdivision DE_CW_N4.9500.03.02
DE_CW_N4.9500.03.02
ANS DE SD_Subdivision DE_CW_N4_3100_01
EN_CW_N4_3100_01
ANS DE SD_Subdivision DE_CW_N4_4900_01
EN_CW_N4_4900_01
ANS DE SD_Subdivision DE_CW_N4_4900_02
EN_CW_N4_4900_02
ANS DE SD_Subdivision DE_CW_N4_5900_01
EN_CW_N4_5900_01
ANS DE SD_Subdivision DE_CW_N5.5000.04.03
DE_CW_N5.5000.04.03
Region/ subregion
ANS
Art. 8 countries involved
DE, UK, DK, BE, NL, SE, NO, , , FR
Art. 8 nature of coordination
1. There has been a high level of information sharing and joint assessment in the North-East Atlantic through the work of the OSPAR Commission. 2. The OSPAR Intermediate Assessment (IA) 2017 provides a basis for coordination of national assessments across the North-East Atlantic . OSPAR Contracting Parties (CP’s) that are also EU Member States have the opportunity to use the information presented in the IA 2017 for their update in 2018 to the EU on the initial assessment (2012) for the MSFD. However, it should be noted that at this point in time, OSPAR IA 2017 indicator assessment values are not necessarily equivalent to EU MSFD criteria threshold values. 3. The IA 2017 is a summary of the current understanding and knowledge supporting the implementation of the OSPAR Thematic Strategies. It is a compilation of 47 assessments that demonstrates the close cooperation and coordination between OSPAR CP’s, as well as with other regional organisations. 4. The IA 2017 builds on assessment processes developed by OSPAR over many years and includes the assessment of recently developed new indicators e.g. in the field of biodiversity, marine litter and underwater noise. The EcApRHA project, co-financed by the EU DG Environment, has significantly contributed to the development of regional indicators for pelagic habitats, benthic habitats and food webs. 5. The IA 2017 presents new and developing aspects in the areas of socio-economics and ecosystem assessment of the OSPAR area. Both areas are of increasing relevance, but a common typology and methodology among OSPAR CP’s needs further development. The next OSPAR Quality Status Report (QSR) could capture such descriptions. 6. OSPAR has developed an assessment portal and a data and information portal, which will enable better collaboration and data exchange between CP’s and other organisations, and support the EU MSFD-reporting obligation. 7. There is still a lack of harmonized valuation methods and indicator assessment values for a number of indicators. Therefore the national Initial Assessments are not always comparable. However, so far no country has flagged major inconsistencies in the conclusions of neighbouring national initial assessments.
Art. 8 regional coherence
Partial
Art. 8 regional coherence problems
As the IA2017 lacks regionally agreed threshold values for some indicators, GES determinations and the integration of indicator assessment results, it does not always provide robust conclusions on the quality status of OSPAR waters. Therefore, EU Member States had to strike a balance between the need to nationally express the extent to which GES has been achieved, in order to meet MSFD requirements, and the degree to which the regionally coordinated IA2017 could be used in this process.
Art. 9 countries involved
UK, DK, BE, NL, SE, NO, , , FR
Art. 9 nature of coordination
1. There has been a moderate level of information sharing in the development of coherent good environmental status (GES) determinations at descriptor and criteria level through the OSPAR Commission. 2. OSPAR supports the cooperation between EU Member States towards coherent and measurable determinations of GES - where possible and appropriate - based on the best available knowledge. The ICG-MSFD will continue to identify opportunities for (sub)regionally coherent GES determinations and common GES determinations where appropriate inter alia on the basis of the agreed common indicators.. 3. In the process of updating the EU GES Commission Decision (2017/848/EU) OSPAR Contracting Parties have collaborated and jointly contributed to the process from the OSPAR perspective. 4. The current assessment values that have been proposed during development of the OSPAR indicators as part of IA 2017, remain exploratory, and may be revised in advance of any subsequent OSPAR assessment. Furthermore, such values are not systematically indicative of GES under the MSFD. 5. In 2017/2018. an analysis was conducted in order to assess the fit of the existing OSPAR indicators with the GES Commission Decision. Mismatches and gaps were identified regarding criteria, lists of elements, threshold values and integration / aggregation rules. Resources needed to develop the required solutions have been estimated. The OSPAR Commission agreed the priority is to address the Primary Criteria as described in the Commission Decision. From 2018 onwards OSPAR Committees will be working to address the requirements of the Commission Decision.
Art. 9 regional coherence
Partial
Art. 9 regional coherence problems
After the adoption of the GES Commission Decision there was no time left for joint work on GES determinations because member states were focusing efforts on national reporting. There is lack of scientific knowledge, consensus on methodologies and/or political support for setting coordinated, quantified threshold values and GES determinations.
Art. 10 countries involved
IT, PL, UK, CZ, DK, BE, CH, AT, NL, SE, NO, , , FR, LU, LI
Art. 10 nature of coordination
1. There has been a low level of information sharing on the development of coordinated environmental targets and indicators. 2. OSPAR aims to contribute to strengthening regional coordination in the implementation of the MSFD and to ensuring coherence with regard to the establishment of environmental targets. 3. In 2018/2019 ICG-MSFD will share information on national targets for five Descriptors, or parts of Descriptors (marine litter, mobile species, non-indigenous species, underwater noise and nutrients) and develop a way forward towards coherent environmental targets in the third cycle of the MSFD. 4. OSPAR strives towards more coordination between its North-East Atlantic Environment Strategy and environmental targets set for the implementation of the MSFD.
Art. 10 regional coherence
Partial
Art. 10 regional coherence problems
OSPAR aims to contribute to strengthening regional coordination of implementation of the MSFD and to ensuring coherence with regard to the establishment of environmental targets. However, the timing of a joint effort was not because CP’s that are EU Member States were focused on the update of the Commission Decision (2017/848/EU). After the adoption of the Commission Decision there was no time for setting joint ambitions because member states were focusing efforts on national reporting. There is lack of scientific knowledge, consensus on methodologies and/or political support for setting coordinated quantified and specific targets. Furthermore, each CP may have specific process to involve local stakeholders in environmental targets definition. It can be challenging to converge on common environmental targets that are endorsed both at a local, national and (sub)regional level.

Report type Member State report to Commission
MSFD Article Art. 3(1) Marine waters & Art. 4/2017 Decision: Marine regions, subregions, and subdivisions & Art. 5(2) & Art. 6 Regional cooperation
Member State Germany
Reported by Bundesministerium fuer Umwelt, Naturschutz und nukleare Sicherheit
Report date 2019-01-28
Report access ANSDE_MSFD4Geo_20190128.xml
Member state marine waters
The German marine waters including the seabed and subsoil relate to the German part of the North Sea and Baltic sea. The outer limit of the area are identical with the Exclusive Economic Zone (EEZ).
Region / subregion description
The German Subregion ANSDE and BALDE cover the German part of the North Sea and the Baltic Sea.
Subdivisions
Germany defined for the 2018 reporting new assessment scales on selected GES criteria. For these criteria the following area types have been choosen: Territorial waters as defined under the WFD, Coastal waters as defined under the WFD, Fishing area, MS marine waters part of a Region or Subregion. Because of the fact that these area types are not part of the area type codelist of the MSFD4geo schema Germany mapped them to 'SD_Subdivision' and 'MS_PartRegionSubregion'.
MRUs description (AreaType)
No formal assessment areas have been defined.
MRUs
Region or subregion Member state Area type Marine Reporting Unit MRU Name
ANS DE SD_Subdivision ANSDE_BRG
ANSDE_BRG
ANS DE SD_Subdivision ANSDE_CW
ANSDE_CW
ANS DE SD_Subdivision ANSDE_D5_EF12
ANSDE_D5_EF12
ANS DE SD_Subdivision ANSDE_D5_EF34
ANSDE_D5_EF34
ANS DE SD_Subdivision ANSDE_D5_EW34
ANSDE_D5_EW34
ANS DE SD_Subdivision ANSDE_D5_ICEF
ANSDE_D5_ICEF
ANS DE SD_Subdivision ANSDE_D5_ICNF
ANSDE_D5_ICNF
ANS DE SD_Subdivision ANSDE_D5_NF12
ANSDE_D5_NF12
ANS DE SD_Subdivision ANSDE_D5_OCEF
ANSDE_D5_OCEF
ANS DE SD_Subdivision ANSDE_D5_OCNF
ANSDE_D5_OCNF
ANS DE SD_Subdivision ANSDE_D5_OFFI
ANSDE_D5_OFFI
ANS DE SD_Subdivision ANSDE_D5_OFFO
ANSDE_D5_OFFO
ANS DE SD_Subdivision ANSDE_DBN
ANSDE_DBN
ANS DE SD_Subdivision ANSDE_DBS
ANSDE_DBS
ANS DE SD_Subdivision ANSDE_EEZ
ANSDE_EEZ
ANS DE SD_Subdivision ANSDE_EUT
ANSDE_EUT
ANS DE MS_MarineWatersPartRegionSubregion ANSDE_MS
ANSDE_MS
ANS DE SD_Subdivision ANSDE_ODB
ANSDE_ODB
ANS DE SD_Subdivision ANSDE_TeW
ANSDE_TeW
ANS DE SD_Subdivision ANSDE_offshore
ANSDE_offshore
ANS DE SD_Subdivision DE_CW_N0.3900
DE_CW_N0.3900
ANS DE SD_Subdivision DE_CW_N0.3990
DE_CW_N0.3990
ANS DE SD_Subdivision DE_CW_N0.4000
DE_CW_N0.4000
ANS DE SD_Subdivision DE_CW_N0.5000
DE_CW_N0.5000
ANS DE SD_Subdivision DE_CW_N0.9500
DE_CW_N0.9500
ANS DE SD_Subdivision DE_CW_N1.9500.01.01
DE_CW_N1.9500.01.01
ANS DE SD_Subdivision DE_CW_N1.9500.01.02
DE_CW_N1.9500.01.02
ANS DE SD_Subdivision DE_CW_N1_3100_01
EN_CW_N1_3100_01
ANS DE SD_Subdivision DE_CW_N1_4900_01
EN_CW_N1_4900_01
ANS DE SD_Subdivision DE_CW_N2.9500.01.03
DE_CW_N2.9500.01.03
ANS DE SD_Subdivision DE_CW_N2.9500.01.04
DE_CW_N2.9500.01.04
ANS DE SD_Subdivision DE_CW_N2.9500.01.05
DE_CW_N2.9500.01.05
ANS DE SD_Subdivision DE_CW_N2.9500.01.06
DE_CW_N2.9500.01.06
ANS DE SD_Subdivision DE_CW_N2_3100_01
EN_CW_N2_3100_01
ANS DE SD_Subdivision DE_CW_N2_4900_01
EN_CW_N2_4900_01
ANS DE SD_Subdivision DE_CW_N3.5000.04.01
DE_CW_N3.5000.04.01
ANS DE SD_Subdivision DE_CW_N3.9500.02.01
DE_CW_N3.9500.02.01
ANS DE SD_Subdivision DE_CW_N3.9500.03.01
DE_CW_N3.9500.03.01
ANS DE SD_Subdivision DE_CW_N3_3990_01
EN_CW_N3_3990_01
ANS DE SD_Subdivision DE_CW_N3_4900_01
EN_CW_N3_4900_01
ANS DE SD_Subdivision DE_CW_N4.5000.04.02
DE_CW_N4.5000.04.02
ANS DE SD_Subdivision DE_CW_N4.9500.02.02
DE_CW_N4.9500.02.02
ANS DE SD_Subdivision DE_CW_N4.9500.03.02
DE_CW_N4.9500.03.02
ANS DE SD_Subdivision DE_CW_N4_3100_01
EN_CW_N4_3100_01
ANS DE SD_Subdivision DE_CW_N4_4900_01
EN_CW_N4_4900_01
ANS DE SD_Subdivision DE_CW_N4_4900_02
EN_CW_N4_4900_02
ANS DE SD_Subdivision DE_CW_N4_5900_01
EN_CW_N4_5900_01
ANS DE SD_Subdivision DE_CW_N5.5000.04.03
DE_CW_N5.5000.04.03
Region/ subregion
ANS
Art. 8 countries involved
DE, UK, DK, BE, NL, SE, NO, , , FR
Art. 8 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" Intensive exchange of information: Development of joint assessment bases and joint assessment at the level of the OSPAR Commission for the Protection of the Marine Environment of the Northeast Atlantic. At this level, integrated environmental assessments have repeatedly been carried out to create thematic assessment reports as the basis of the OSPAR Quality Status Report (QSR) 2010. The QSR 2010 and the underlying assessment reports are the basis for the coordination of the national initial assessments at OSPAR level. The QSR provides a comprehensive summary of the environmental status of the Northeast Atlantic and its five sub-regions including the North Sea. In this respect, it is the proof of the coherence of the initial assessments at the level of the North Sea sub-region as well as the North-East Atlantic region. With regard to the national conclusions of the initial assessment, it was agreed to carry out the coordination between the contracting parties concerned at the sub-region level. Another basis was the report on the ecological status of the Wadden Sea 2009 (QSR 2009). QSRs are regularly created by the trilateral Wadden Sea Cooperation between Denmark, the Netherlands and Germany (Trilateral Wadden Sea Cooperation, TWSC). OSPAR bodies have developed internal "Advice Documents", among other things for the development of assessment procedures and indicators. The "Advice Documents" for descriptors 1, 2, 4 and 6 together as well as for descriptors 5, 7, 8 and 10 are available on the CIRCA website. In these documents, all available information (national, EU) has been taken into account. For descriptors 1, 2, 4 and 6, the national approaches for assessment procedures within the framework of the Intersessional Correspondence Group on the Coordination of Biodiversity Assessment and Monitoring (ICG-COBAM) investigated and coordinated. This includes the development of a common set of regional core indicators. The economic and social analysis of the use of the North Sea waters under German sovereignty is uncharted territory. The necessary coordination with regard to the methodological approaches to be pursued took place across the EU within the framework of the CIS working group ESA. In addition, a pilot study is currently taking place within the framework of OSPAR, which serves the purpose of further coordination. In addition to this multilateral coordination, bilateral coordination took place on October 11, 2011 with the UK and on November 25, 2011 with NL. Bilateral coordination with DK is currently being planned. The results of the initial assessments are comparable. However, the Wadden Sea is not considered by NL. Both UK and NL have more experience of economic and social analysis. A first comparison with DK positions took place within the framework of a multilateral coordination (BE, DE, DK, FR , UK, NL).
Art. 8 regional coherence
Partial
Art. 8 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive (MSFD) makes coordination more difficult. The above-mentioned set of regional core indicators, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between OSPAR and EU procedures is also required.
Art. 9 countries involved
UK, DK, BE, NL, SE, NO, , , FR
Art. 9 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" The OSPAR contracting parties have intensively exchanged information on existing methods for describing good environmental status and coordinated their further development at OSPAR level. OSPAR bodies have internal "Advice Documents" for describing good environmental status and defining Goals and indicators developed. The "Advice Documents" for descriptors 1, 2, 4 and 6 together as well as for descriptors 5, 7, 8 and 10 are available on the CIRCA website. In these documents, all available information (national, EU) has been taken into account. For descriptors 1, 2, 4 and 6, the national approaches for good environmental status within the framework of the Intersessional Correspondence Group on the Coordination of Biodiversity Assessment and Monitoring (ICG- COBAM) investigated and coordinated. This includes the development of a common regional set of core indicators. The descriptions of the good environmental status were created at OSPAR level on the basis of an inventory of the national drafts for Articles 9 and 10 with regard to descriptors 3, 5, 7, 8, 9, 10 and 11 and jointly analyzed with regard to regional coherence. The evaluation ranged from good (D 5, 8, 9, 10) to adequate (D 3, 11) to poor (D 7) coordination. In order to improve regional coordination, a number of improvement measures to be implemented directly or after July 2012 were identified. In addition to this multilateral coordination, bilateral coordination took place on October 11, 2011 with GB and on November 25, 2011 with NL. A first comparison with DK positions took place within the framework of a multilateral coordination (BE, DE, DK, FR, GB, NL) carried out in The Hague on June 15, 2012 at the invitation of NL. In contrast to DE, UK and NL summarize GES and environmental objectives in one report or chapter, with NL also summarizing descriptors 1, 3, 4 and 6 as the descriptor "Marine Ecosystem".
Art. 9 regional coherence
Partial
Art. 9 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned (possibly regional) core indicator sets, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between HELCOM and EU procedures is also necessary.
Art. 10 countries involved
IT, PL, UK, CZ, DK, BE, CH, AT, NL, SE, NO, , , FR, LU, LI
Art. 10 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" The OSPAR contracting parties have exchanged views on the development of coordinated environmental targets and indicators. The OSPAR bodies have developed internal "Advice Documents" to describe the good status and to define targets and indicators. The "Advice Documents" for descriptors 1, 2, 4 and 6 together as well as for descriptors 5, 7, 8 and 10 are available on the CIRCA website. All available information (national, EU) has been taken into account in these documents. Environmental targets were set at OSPAR level on the basis of an inventory of national drafts for Articles 9 and 10 with regard to descriptors 3, 5, 7, 8, 9 , 10 and 11 and analyzed together with regard to regional coherence. The evaluation ranged from good (D 5, 8, 9, 10) to adequate (D 3, 11) to poor (D 7) coordination. In order to improve regional coordination, a number of improvement measures to be implemented directly or after July 2012 were identified. For descriptors 1, 2, 4 and 6, the national approaches for biodiversity targets and indicators within the framework of the Intersessional Correspondence Group were on the Coordination of Biodiversity Assessment and Monitoring (ICG-COBAM) investigates and coordinates. This includes the development of a common set of regional core indicators. Further bases were the work of the trilateral Wadden Sea Cooperation between Denmark, the Netherlands and Germany (Trilateral Wadden Sea Cooperation, TWSC). In addition to this multilateral coordination, bilateral coordination took place on October 11, 2011 with the UK and on November 25th, 2011 with NL. A first comparison with DK positions took place within the framework of a multilateral coordination (BE, DE, DK, FR, UK, NL) carried out on June 15, 2012 in The Hague at the invitation of NL. In contrast to DE, UK and NL GES and environmental goals together in a report or chapter, with NL additionally summarizing the descriptors 1, 3, 4 and 6 as the descriptor "Marine Ecosystem". With regard to the environmental objectives and indicators, DE follows a similar approach to the NL approach mentioned last, but in which descriptors 1, 2, 4 and 6 are combined in one chapter. Coordination with (member) states in the catchment area without marine waters takes place as far as necessary , via the International Commissions for the Protection of the Elbe (IKSE) and the Rhine (IKSR).
Art. 10 regional coherence
Partial
Art. 10 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned set of regional core indicators, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between OSPAR and EU procedures is also required.

Report type Member State report to Commission
MSFD Article Art. 3(1) Marine waters & Art. 4/2017 Decision: Marine regions, subregions, and subdivisions & Art. 5(2) & Art. 6 Regional cooperation
Member State Germany
Reported by Bundesministerium fuer Umwelt, Naturschutz und nukleare Sicherheit
Report date 2019-01-28
Report access BALDE_MSFD4Geo_20190128.xml
Member state marine waters
The German marine waters including the seabed and subsoil relate to the German part of the North Sea and Baltic sea. The outer limit of the area are identical with the Exclusive Economic Zone (EEZ).
Region / subregion description
The German Subregion ANSDE and BALDE cover the German part of the North Sea and the Baltic Sea.
Subdivisions
Germany defined for the 2018 reporting new assessment scales on selected GES criteria. For these criteria the following area types have been choosen: Territorial waters as defined under the WFD, Coastal waters as defined under the WFD, Fishing area, MS marine waters part of a Region or Subregion. Because of the fact that these area types are not part of the area type codelist of the MSFD4geo schema Germany mapped them to 'SD_Subdivision' and 'MS_PartRegionSubregion'.
MRUs description (AreaType)
No formal assessment areas have been defined.
MRUs
Region or subregion Member state Area type Marine Reporting Unit MRU Name
BAL DE SD_Subdivision BALDE_CW
BALDE_CW
BAL DE SD_Subdivision BALDE_CW_AB
BALDE_CW_AB
BAL DE SD_Subdivision BALDE_CW_BB
BALDE_CW_BB
BAL DE SD_Subdivision BALDE_CW_D5_AB_B2
BALDE_CW_D5_AB_B2
BAL DE SD_Subdivision BALDE_CW_D5_AB_B3
BALDE_CW_D5_AB_B3
BAL DE SD_Subdivision BALDE_CW_D5_BB_B2
BALDE_CW_D5_BB_B2
BAL DE SD_Subdivision BALDE_CW_D5_BB_B3
BALDE_CW_D5_BB_B3
BAL DE SD_Subdivision BALDE_CW_D5_GB_B3
BALDE_CW_D5_GB_B3
BAL DE SD_Subdivision BALDE_CW_D5_KB_B2
BALDE_CW_D5_KB_B2
BAL DE SD_Subdivision BALDE_CW_D5_KB_B3
BALDE_CW_D5_KB_B3
BAL DE SD_Subdivision BALDE_CW_D5_MB_B2
BALDE_CW_D5_MB_B2
BAL DE SD_Subdivision BALDE_CW_D5_MB_B3
BALDE_CW_D5_MB_B3
BAL DE SD_Subdivision BALDE_CW_KB
BALDE_CW_KB
BAL DE SD_Subdivision BALDE_CW_MB
BALDE_CW_MB
BAL DE SD_Subdivision BALDE_EEZ
BALDE_EEZ
BAL DE SD_Subdivision BALDE_EEZ_AB
BALDE_EEZ_AB
BAL DE SD_Subdivision BALDE_EEZ_BB
BALDE_EEZ_BB
BAL DE SD_Subdivision BALDE_EEZ_KB
BALDE_EEZ_KB
BAL DE SD_Subdivision BALDE_EEZ_MB
BALDE_EEZ_MB
BAL DE SD_Subdivision BALDE_FA_3c22
BALDE_FA_3c22
BAL DE SD_Subdivision BALDE_FA_3d24
BALDE_FA_3d24
BAL DE MS_MarineWatersPartRegionSubregion BALDE_MS
BALDE_MS
BAL DE SD_Subdivision BALDE_OFFSHORE_AB
BALDE_OFFSHORE_AB
BAL DE SD_Subdivision BALDE_OFFSHORE_BB
BALDE_OFFSHORE_BB
BAL DE SD_Subdivision BALDE_OFFSHORE_KB
BALDE_OFFSHORE_KB
BAL DE SD_Subdivision BALDE_OFFSHORE_MB
BALDE_OFFSHORE_MB
BAL DE SD_Subdivision DE_CW_B0.9610
DE_CW_B0.9610
BAL DE SD_Subdivision DE_CW_B2.9610.07.01
DE_CW_B2.9610.07.01
BAL DE SD_Subdivision DE_CW_B2.9610.07.02
DE_CW_B2.9610.07.02
BAL DE SD_Subdivision DE_CW_B2.9610.07.03
DE_CW_B2.9610.07.03
BAL DE SD_Subdivision DE_CW_B2.9610.07.04
DE_CW_B2.9610.07.04
BAL DE SD_Subdivision DE_CW_B2.9610.09.01
DE_CW_B2.9610.09.01
BAL DE SD_Subdivision DE_CW_B2.9610.09.02
DE_CW_B2.9610.09.02
BAL DE SD_Subdivision DE_CW_B2.9610.10.01
DE_CW_B2.9610.10.01
BAL DE SD_Subdivision DE_CW_B2.9610.10.02
DE_CW_B2.9610.10.02
BAL DE SD_Subdivision DE_CW_B2.9610.10.03
DE_CW_B2.9610.10.03
BAL DE SD_Subdivision DE_CW_B3.9610.07.05
DE_CW_B3.9610.07.05
BAL DE SD_Subdivision DE_CW_B3.9610.07.06
DE_CW_B3.9610.07.06
BAL DE SD_Subdivision DE_CW_B3.9610.07.07
DE_CW_B3.9610.07.07
BAL DE SD_Subdivision DE_CW_B3.9610.09.03
DE_CW_B3.9610.09.03
BAL DE SD_Subdivision DE_CW_B3.9610.09.04
DE_CW_B3.9610.09.04
BAL DE SD_Subdivision DE_CW_B3.9610.09.05
DE_CW_B3.9610.09.05
BAL DE SD_Subdivision DE_CW_B3.9610.09.06
DE_CW_B3.9610.09.06
BAL DE SD_Subdivision DE_CW_B3.9610.09.07
DE_CW_B3.9610.09.07
BAL DE SD_Subdivision DE_CW_B3.9610.09.08
DE_CW_B3.9610.09.08
BAL DE SD_Subdivision DE_CW_B3.9610.09.09
DE_CW_B3.9610.09.09
BAL DE SD_Subdivision DE_CW_B4.9610.07.08
DE_CW_B4.9610.07.08
BAL DE SD_Subdivision DE_CW_B4.9610.07.09
DE_CW_B4.9610.07.09
BAL DE SD_Subdivision DE_CW_B4.9610.09.10
DE_CW_B4.9610.09.10
BAL DE SD_Subdivision DE_CW_B4.9610.09.11
DE_CW_B4.9610.09.11
BAL DE SD_Subdivision DE_CW_B4.9610.09.12
DE_CW_B4.9610.09.12
BAL DE SD_Subdivision DE_CW_DEMV_OD_01
DE_CW_DEMV_OD_01
BAL DE SD_Subdivision DE_CW_DEMV_WP_01
DE_CW_DEMV_WP_01
BAL DE SD_Subdivision DE_CW_DEMV_WP_02
DE_CW_DEMV_WP_02
BAL DE SD_Subdivision DE_CW_DEMV_WP_03
DE_CW_DEMV_WP_03
BAL DE SD_Subdivision DE_CW_DEMV_WP_04
DE_CW_DEMV_WP_04
BAL DE SD_Subdivision DE_CW_DEMV_WP_05
DE_CW_DEMV_WP_05
BAL DE SD_Subdivision DE_CW_DEMV_WP_06
DE_CW_DEMV_WP_06
BAL DE SD_Subdivision DE_CW_DEMV_WP_07
DE_CW_DEMV_WP_07
BAL DE SD_Subdivision DE_CW_DEMV_WP_08
DE_CW_DEMV_WP_08
BAL DE SD_Subdivision DE_CW_DEMV_WP_09
DE_CW_DEMV_WP_09
BAL DE SD_Subdivision DE_CW_DEMV_WP_10
DE_CW_DEMV_WP_10
BAL DE SD_Subdivision DE_CW_DEMV_WP_11
DE_CW_DEMV_WP_11
BAL DE SD_Subdivision DE_CW_DEMV_WP_12
DE_CW_DEMV_WP_12
BAL DE SD_Subdivision DE_CW_DEMV_WP_13
DE_CW_DEMV_WP_13
BAL DE SD_Subdivision DE_CW_DEMV_WP_14
DE_CW_DEMV_WP_14
BAL DE SD_Subdivision DE_CW_DEMV_WP_15
DE_CW_DEMV_WP_15
BAL DE SD_Subdivision DE_CW_DEMV_WP_16
DE_CW_DEMV_WP_16
BAL DE SD_Subdivision DE_CW_DEMV_WP_17
DE_CW_DEMV_WP_17
BAL DE SD_Subdivision DE_CW_DEMV_WP_18
DE_CW_DEMV_WP_18
BAL DE SD_Subdivision DE_CW_DEMV_WP_19
DE_CW_DEMV_WP_19
BAL DE SD_Subdivision DE_CW_DEMV_WP_20
DE_CW_DEMV_WP_20
BAL DE SD_Subdivision DE_CW_DEMV_WP_21
DE_CW_DEMV_WP_21
Region/ subregion
BAL
Art. 8 countries involved
EE, DE, PL, LT, FI, DK, SE, RU, LV, ,
Art. 8 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" Intensive exchange of information: Development of joint assessment bases and joint assessment at the level of the Helsinki Commission (HELCOM) for the protection of the marine environment in the Baltic Sea area. At this level, integrated environmental assessments have repeatedly been carried out to create thematic assessment reports as the basis for the comprehensive assessment of the marine environment of the Baltic Sea (HELCOM HOLAS, 2010). The HOLAS report and the underlying assessment reports are the basis for the coordination of the national initial assessments at HELCOM level. The HOLAS report 2010 provides an overarching summary of the state of the marine environment in the Baltic Sea area. It is the starting point for the coordination of the initial assessment of the countries bordering the Baltic Sea and covers the four areas of nutrient inputs, hazardous substances, biodiversity and maritime shipping. There is also a chapter on costs and benefits. Based on the HOLAS report for the initial evaluations, the coherence in the area of ​​the regions is ensured. Separate bilateral agreements between the states concerned have taken place on individual sub-regions, so that further harmonization has also taken place in this area. In addition, intensive harmonization efforts are taking place within the framework of the HELCOM projects to develop a core indicator set (CORESET) and to review the ecological goals of the Baltic Sea Action Plan regarding eutrophication (TARGREV). In this context, HELCOM is currently developing core indicator sets with regard to biodiversity, hazardous substances and eutrophication. The economic and social analysis of the use of the Baltic Sea waters under German jurisdiction is uncharted territory. The necessary coordination with regard to the methodological approaches to be pursued took place across the EU within the framework of the CIS working group ESA. In addition to this multilateral coordination, trilateral coordination with DK and PL is currently being planned. It is known from the HELCOM cooperation that the results of the initial assessments are comparable.
Art. 8 regional coherence
Partial
Art. 8 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned (possibly regional) core indicator sets, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between HELCOM and EU procedures is also necessary.
Art. 9 countries involved
EE, DE, PL, LT, FI, DK, SE, RU, LV, ,
Art. 9 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" At HELCOM there was an intensive exchange about existing methods for describing the good condition as well as the coordination of their further development. As part of the HELCOM projects to develop a core set of indicators (CORESET) and to review the ecological goals of the Baltic Sea Action Plan with regard to eutrophication (TARGREV), core sets of indicators are being developed with regard to biodiversity, hazardous substances and eutrophication. These core indicators also contain goals or limits to determine when good environmental status has been achieved. At the time of reporting, the results from TARGREV are still the subject of national and regional discussions. Both projects were accompanied by a Joint Advisory Board (JAB) in which all member states were represented and to ensure that uniform principles are applied throughout the Baltic Sea. JAB also served as a platform for the exchange of national activities for the implementation of the Marine Strategy Framework Directive (MSFD) and has now been replaced by the group for the implementation of the ecosystem approach (GEAR). At the time of reporting, activities at HELCOM are ongoing to inventory the national approaches for the implementation of Articles 8, 9 and 10 MSFD and to assess the state of coordination. In addition to this multilateral coordination, trilateral coordination with DK and PL is currently being planned. In addition, details were also agreed in bilateral country meetings.
Art. 9 regional coherence
Partial
Art. 9 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned (possibly regional) core indicator sets, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between HELCOM and EU procedures is also necessary.
Art. 10 countries involved
EE, DE, PL, LT, FI, DK, SE, RU, LV, ,
Art. 10 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" At HELCOM there was an intensive exchange about existing methods for describing the good condition as well as the coordination of their further development. The basis for this is the HELCOM Baltic Sea Action Plan (BSAP), which was adopted in 2007. The Baltic Sea Action Plan deals with all major environmental problems that can affect the marine environment in the Baltic Sea and provides specific goals to counter them. The far-reaching campaigns build on the extensive and long-term cooperation within HELCOM. As part of the HELCOM projects to develop a core set of indicators (CORESET) and to review the ecological goals of the Baltic Sea Action Plan with regard to eutrophication (TARGREV), core sets of indicators are being developed with regard to biodiversity, hazardous substances and eutrophication. These core indicator sets also contain goals or limits to determine when good environmental status has been achieved. At the time of reporting, the results from TARGREV are still the subject of national and regional discussions. Both projects were accompanied by a Joint Advisory Board (JAB) in which all member states were represented and to ensure that uniform principles are applied throughout the Baltic Sea. JAB also served as a platform for the exchange of national activities for the implementation of the Marine Strategy Framework Directive (MSFD) and has now been replaced by the group for the implementation of the ecosystem approach (GEAR). At the time of reporting, activities at HELCOM are ongoing to inventory the national approaches for the implementation of Articles 8, 9 and 10 MSFD and to assess the state of coordination. In addition to this multilateral coordination, trilateral coordination with DK and POL is currently being planned. In addition, details were also agreed in bilateral country meetings. Coordination with CZ as a member state in the catchment area without marine waters takes place, as far as necessary, via the International Commission for the Protection of the Oder (IKSO).
Art. 10 regional coherence
Partial
Art. 10 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned (possibly regional) core indicator sets, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between HELCOM and EU procedures is also necessary.

Report type Member State report to Commission
MSFD Article Art. 3(1) Marine waters & Art. 4/2017 Decision: Marine regions, subregions, and subdivisions & Art. 5(2) & Art. 6 Regional cooperation
Member State Germany
Reported by Bundesministerium fuer Umwelt, Naturschutz und nukleare Sicherheit
Report date 2018-06-07
Report access ANSDE_MSFD4Geo_20180530.xml
Member state marine waters
The German marine waters including the seabed and subsoil relate to the German part of the North Sea and Baltic sea. The outer limit of the area are identical with the Exclusive Economic Zone (EEZ).
Region / subregion description
The German Subregion ANSDE and BALDE cover the German part of the North Sea and the Baltic Sea.
Subdivisions
Germany defined for the 2018 reporting new assessment scales on selected GES criteria. For these criteria the following area types have been choosen: Territorial waters as defined under the WFD, Coastal waters as defined under the WFD, Fishing area, MS marine waters part of a Region or Subregion. Because of the fact that these area types are not part of the area type codelist of the MSFD4geo schema Germany mapped them to 'SD_Subdivision' and 'MS_PartRegionSubregion'.
MRUs description (AreaType)
No formal assessment areas have been defined.
MRUs
Region or subregion Member state Area type Marine Reporting Unit MRU Name
ANS DE SD_Subdivision ANSDE_BRG
ANSDE_BRG
ANS DE SD_Subdivision ANSDE_CW
ANSDE_CW
ANS DE SD_Subdivision ANSDE_D5_EF12
ANSDE_D5_EF12
ANS DE SD_Subdivision ANSDE_D5_EF34
ANSDE_D5_EF34
ANS DE SD_Subdivision ANSDE_D5_EW34
ANSDE_D5_EW34
ANS DE SD_Subdivision ANSDE_D5_ICEF
ANSDE_D5_ICEF
ANS DE SD_Subdivision ANSDE_D5_ICNF
ANSDE_D5_ICNF
ANS DE SD_Subdivision ANSDE_D5_NF12
ANSDE_D5_NF12
ANS DE SD_Subdivision ANSDE_D5_OCEF
ANSDE_D5_OCEF
ANS DE SD_Subdivision ANSDE_D5_OCNF
ANSDE_D5_OCNF
ANS DE SD_Subdivision ANSDE_D5_OFFI
ANSDE_D5_OFFI
ANS DE SD_Subdivision ANSDE_D5_OFFO
ANSDE_D5_OFFO
ANS DE SD_Subdivision ANSDE_DBN
ANSDE_DBN
ANS DE SD_Subdivision ANSDE_DBS
ANSDE_DBS
ANS DE SD_Subdivision ANSDE_EEZ
ANSDE_EEZ
ANS DE SD_Subdivision ANSDE_EUT
ANSDE_EUT
ANS DE MS_MarineWatersPartRegionSubregion ANSDE_MS
ANSDE_MS
ANS DE SD_Subdivision ANSDE_ODB
ANSDE_ODB
ANS DE SD_Subdivision ANSDE_TeW
ANSDE_TeW
ANS DE SD_Subdivision ANSDE_offshore
ANSDE_offshore
ANS DE SD_Subdivision DE_CW_N0.3900
DE_CW_N0.3900
ANS DE SD_Subdivision DE_CW_N0.3990
DE_CW_N0.3990
ANS DE SD_Subdivision DE_CW_N0.4000
DE_CW_N0.4000
ANS DE SD_Subdivision DE_CW_N0.5000
DE_CW_N0.5000
ANS DE SD_Subdivision DE_CW_N0.9500
DE_CW_N0.9500
ANS DE SD_Subdivision DE_CW_N1.9500.01.01
DE_CW_N1.9500.01.01
ANS DE SD_Subdivision DE_CW_N1.9500.01.02
DE_CW_N1.9500.01.02
ANS DE SD_Subdivision DE_CW_N1_3100_01
EN_CW_N1_3100_01
ANS DE SD_Subdivision DE_CW_N1_4900_01
EN_CW_N1_4900_01
ANS DE SD_Subdivision DE_CW_N2.9500.01.03
DE_CW_N2.9500.01.03
ANS DE SD_Subdivision DE_CW_N2.9500.01.04
DE_CW_N2.9500.01.04
ANS DE SD_Subdivision DE_CW_N2.9500.01.05
DE_CW_N2.9500.01.05
ANS DE SD_Subdivision DE_CW_N2.9500.01.06
DE_CW_N2.9500.01.06
ANS DE SD_Subdivision DE_CW_N2_3100_01
EN_CW_N2_3100_01
ANS DE SD_Subdivision DE_CW_N2_4900_01
EN_CW_N2_4900_01
ANS DE SD_Subdivision DE_CW_N3.5000.04.01
DE_CW_N3.5000.04.01
ANS DE SD_Subdivision DE_CW_N3.9500.02.01
DE_CW_N3.9500.02.01
ANS DE SD_Subdivision DE_CW_N3.9500.03.01
DE_CW_N3.9500.03.01
ANS DE SD_Subdivision DE_CW_N3_3990_01
EN_CW_N3_3990_01
ANS DE SD_Subdivision DE_CW_N3_4900_01
EN_CW_N3_4900_01
ANS DE SD_Subdivision DE_CW_N4.5000.04.02
DE_CW_N4.5000.04.02
ANS DE SD_Subdivision DE_CW_N4.9500.02.02
DE_CW_N4.9500.02.02
ANS DE SD_Subdivision DE_CW_N4.9500.03.02
DE_CW_N4.9500.03.02
ANS DE SD_Subdivision DE_CW_N4_3100_01
EN_CW_N4_3100_01
ANS DE SD_Subdivision DE_CW_N4_4900_01
EN_CW_N4_4900_01
ANS DE SD_Subdivision DE_CW_N4_4900_02
EN_CW_N4_4900_02
ANS DE SD_Subdivision DE_CW_N4_5900_01
EN_CW_N4_5900_01
ANS DE SD_Subdivision DE_CW_N5.5000.04.03
DE_CW_N5.5000.04.03
Region/ subregion
ANS
Art. 8 countries involved
DE, UK, DK, BE, NL, SE, NO, , , FR
Art. 8 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" Intensive exchange of information: Development of joint assessment bases and joint assessment at the level of the OSPAR Commission for the Protection of the Marine Environment of the Northeast Atlantic. At this level, integrated environmental assessments have repeatedly been carried out to create thematic assessment reports as the basis of the OSPAR Quality Status Report (QSR) 2010. The QSR 2010 and the underlying assessment reports are the basis for the coordination of the national initial assessments at OSPAR level. The QSR provides a comprehensive summary of the environmental status of the Northeast Atlantic and its five sub-regions including the North Sea. In this respect, it is the proof of the coherence of the initial assessments at the level of the North Sea sub-region as well as the North-East Atlantic region. With regard to the national conclusions of the initial assessment, it was agreed to carry out the coordination between the contracting parties concerned at the sub-region level. Another basis was the report on the ecological status of the Wadden Sea 2009 (QSR 2009). QSRs are regularly created by the trilateral Wadden Sea Cooperation between Denmark, the Netherlands and Germany (Trilateral Wadden Sea Cooperation, TWSC). OSPAR bodies have developed internal "Advice Documents", among other things for the development of assessment procedures and indicators. The "Advice Documents" for descriptors 1, 2, 4 and 6 together as well as for descriptors 5, 7, 8 and 10 are available on the CIRCA website. In these documents, all available information (national, EU) has been taken into account. For descriptors 1, 2, 4 and 6, the national approaches for assessment procedures within the framework of the Intersessional Correspondence Group on the Coordination of Biodiversity Assessment and Monitoring (ICG-COBAM) investigated and coordinated. This includes the development of a common set of regional core indicators. The economic and social analysis of the use of the North Sea waters under German sovereignty is uncharted territory. The necessary coordination with regard to the methodological approaches to be pursued took place across the EU within the framework of the CIS working group ESA. In addition, a pilot study is currently taking place within the framework of OSPAR, which serves the purpose of further coordination. In addition to this multilateral coordination, bilateral coordination took place on October 11, 2011 with the UK and on November 25, 2011 with NL. Bilateral coordination with DK is currently being planned. The results of the initial assessments are comparable. However, the Wadden Sea is not considered by NL. Both UK and NL have more experience of economic and social analysis. A first comparison with DK positions took place within the framework of a multilateral coordination (BE, DE, DK, FR , UK, NL).
Art. 8 regional coherence
Partial
Art. 8 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive (MSFD) makes coordination more difficult. The above-mentioned set of regional core indicators, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between OSPAR and EU procedures is also required.
Art. 9 countries involved
UK, DK, BE, NL, SE, NO, , , FR
Art. 9 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" The OSPAR contracting parties have intensively exchanged information on existing methods for describing good environmental status and coordinated their further development at OSPAR level. OSPAR bodies have internal "Advice Documents" for describing good environmental status and defining Goals and indicators developed. The "Advice Documents" for descriptors 1, 2, 4 and 6 together as well as for descriptors 5, 7, 8 and 10 are available on the CIRCA website. In these documents, all available information (national, EU) has been taken into account. For descriptors 1, 2, 4 and 6, the national approaches for good environmental status within the framework of the Intersessional Correspondence Group on the Coordination of Biodiversity Assessment and Monitoring (ICG- COBAM) investigated and coordinated. This includes the development of a common regional set of core indicators. The descriptions of the good environmental status were created at OSPAR level on the basis of an inventory of the national drafts for Articles 9 and 10 with regard to descriptors 3, 5, 7, 8, 9, 10 and 11 and jointly analyzed with regard to regional coherence. The evaluation ranged from good (D 5, 8, 9, 10) to adequate (D 3, 11) to poor (D 7) coordination. In order to improve regional coordination, a number of improvement measures to be implemented directly or after July 2012 were identified. In addition to this multilateral coordination, bilateral coordination took place on October 11, 2011 with GB and on November 25, 2011 with NL. A first comparison with DK positions took place within the framework of a multilateral coordination (BE, DE, DK, FR, GB, NL) carried out in The Hague on June 15, 2012 at the invitation of NL. In contrast to DE, UK and NL summarize GES and environmental objectives in one report or chapter, with NL also summarizing descriptors 1, 3, 4 and 6 as the descriptor "Marine Ecosystem".
Art. 9 regional coherence
Partial
Art. 9 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned (possibly regional) core indicator sets, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between HELCOM and EU procedures is also necessary.
Art. 10 countries involved
IT, PL, UK, CZ, DK, BE, CH, AT, NL, SE, NO, , , FR, LU, LI
Art. 10 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" The OSPAR contracting parties have exchanged views on the development of coordinated environmental targets and indicators. The OSPAR bodies have developed internal "Advice Documents" to describe the good status and to define targets and indicators. The "Advice Documents" for descriptors 1, 2, 4 and 6 together as well as for descriptors 5, 7, 8 and 10 are available on the CIRCA website. All available information (national, EU) has been taken into account in these documents. Environmental targets were set at OSPAR level on the basis of an inventory of national drafts for Articles 9 and 10 with regard to descriptors 3, 5, 7, 8, 9 , 10 and 11 and analyzed together with regard to regional coherence. The evaluation ranged from good (D 5, 8, 9, 10) to adequate (D 3, 11) to poor (D 7) coordination. In order to improve regional coordination, a number of improvement measures to be implemented directly or after July 2012 were identified. For descriptors 1, 2, 4 and 6, the national approaches for biodiversity targets and indicators within the framework of the Intersessional Correspondence Group were on the Coordination of Biodiversity Assessment and Monitoring (ICG-COBAM) investigates and coordinates. This includes the development of a common set of regional core indicators. Further bases were the work of the trilateral Wadden Sea Cooperation between Denmark, the Netherlands and Germany (Trilateral Wadden Sea Cooperation, TWSC). In addition to this multilateral coordination, bilateral coordination took place on October 11, 2011 with the UK and on November 25th, 2011 with NL. A first comparison with DK positions took place within the framework of a multilateral coordination (BE, DE, DK, FR, UK, NL) carried out on June 15, 2012 in The Hague at the invitation of NL. In contrast to DE, UK and NL GES and environmental goals together in a report or chapter, with NL additionally summarizing the descriptors 1, 3, 4 and 6 as the descriptor "Marine Ecosystem". With regard to the environmental objectives and indicators, DE follows a similar approach to the NL approach mentioned last, but in which descriptors 1, 2, 4 and 6 are combined in one chapter. Coordination with (member) states in the catchment area without marine waters takes place as far as necessary , via the International Commissions for the Protection of the Elbe (IKSE) and the Rhine (IKSR).
Art. 10 regional coherence
Partial
Art. 10 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned set of regional core indicators, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between OSPAR and EU procedures is also required.

Report type Member State report to Commission
MSFD Article Art. 3(1) Marine waters & Art. 4/2017 Decision: Marine regions, subregions, and subdivisions & Art. 5(2) & Art. 6 Regional cooperation
Member State Germany
Reported by Bundesministerium fuer Umwelt, Naturschutz und nukleare Sicherheit
Report date 2018-09-07
Report access BALDE_MSFD4Geo_20180530.xml
Member state marine waters
The German marine waters including the seabed and subsoil relate to the German part of the North Sea and Baltic sea. The outer limit of the area are identical with the Exclusive Economic Zone (EEZ).
Region / subregion description
The German Subregion ANSDE and BALDE cover the German part of the North Sea and the Baltic Sea.
Subdivisions
Germany defined for the 2018 reporting new assessment scales on selected GES criteria. For these criteria the following area types have been choosen: Territorial waters as defined under the WFD, Coastal waters as defined under the WFD, Fishing area, MS marine waters part of a Region or Subregion. Because of the fact that these area types are not part of the area type codelist of the MSFD4geo schema Germany mapped them to 'SD_Subdivision' and 'MS_PartRegionSubregion'.
MRUs description (AreaType)
No formal assessment areas have been defined.
MRUs
Region or subregion Member state Area type Marine Reporting Unit MRU Name
BAL DE SD_Subdivision BALDE_CW_AB
BALDE_CW_AB
BAL DE SD_Subdivision BALDE_CW_BB
BALDE_CW_BB
BAL DE SD_Subdivision BALDE_CW_D5_AB_B2
BALDE_CW_D5_AB_B2
BAL DE SD_Subdivision BALDE_CW_D5_AB_B3
BALDE_CW_D5_AB_B3
BAL DE SD_Subdivision BALDE_CW_D5_BB_B2
BALDE_CW_D5_BB_B2
BAL DE SD_Subdivision BALDE_CW_D5_BB_B3
BALDE_CW_D5_BB_B3
BAL DE SD_Subdivision BALDE_CW_D5_GB_B3
BALDE_CW_D5_GB_B3
BAL DE SD_Subdivision BALDE_CW_D5_KB_B2
BALDE_CW_D5_KB_B2
BAL DE SD_Subdivision BALDE_CW_D5_KB_B3
BALDE_CW_D5_KB_B3
BAL DE SD_Subdivision BALDE_CW_D5_MB_B2
BALDE_CW_D5_MB_B2
BAL DE SD_Subdivision BALDE_CW_D5_MB_B3
BALDE_CW_D5_MB_B3
BAL DE SD_Subdivision BALDE_CW_KB
BALDE_CW_KB
BAL DE SD_Subdivision BALDE_CW_MB
BALDE_CW_MB
BAL DE SD_Subdivision BALDE_EEZ_AB
BALDE_EEZ_AB
BAL DE SD_Subdivision BALDE_EEZ_BB
BALDE_EEZ_BB
BAL DE SD_Subdivision BALDE_EEZ_KB
BALDE_EEZ_KB
BAL DE SD_Subdivision BALDE_EEZ_MB
BALDE_EEZ_MB
BAL DE SD_Subdivision BALDE_FA_3c22
BALDE_FA_3c22
BAL DE SD_Subdivision BALDE_FA_3d24
BALDE_FA_3d24
BAL DE MS_MarineWatersPartRegionSubregion BALDE_MS
BALDE_MS
BAL DE SD_Subdivision BALDE_OFFSHORE_AB
BALDE_OFFSHORE_AB
BAL DE SD_Subdivision BALDE_OFFSHORE_BB
BALDE_OFFSHORE_BB
BAL DE SD_Subdivision BALDE_OFFSHORE_KB
BALDE_OFFSHORE_KB
BAL DE SD_Subdivision BALDE_OFFSHORE_MB
BALDE_OFFSHORE_MB
BAL DE SD_Subdivision DE_CW_B0.9610
DE_CW_B0.9610
BAL DE SD_Subdivision DE_CW_B2.9610.07.01
DE_CW_B2.9610.07.01
BAL DE SD_Subdivision DE_CW_B2.9610.07.02
DE_CW_B2.9610.07.02
BAL DE SD_Subdivision DE_CW_B2.9610.07.03
DE_CW_B2.9610.07.03
BAL DE SD_Subdivision DE_CW_B2.9610.07.04
DE_CW_B2.9610.07.04
BAL DE SD_Subdivision DE_CW_B2.9610.09.01
DE_CW_B2.9610.09.01
BAL DE SD_Subdivision DE_CW_B2.9610.09.02
DE_CW_B2.9610.09.02
BAL DE SD_Subdivision DE_CW_B2.9610.10.01
DE_CW_B2.9610.10.01
BAL DE SD_Subdivision DE_CW_B2.9610.10.02
DE_CW_B2.9610.10.02
BAL DE SD_Subdivision DE_CW_B2.9610.10.03
DE_CW_B2.9610.10.03
BAL DE SD_Subdivision DE_CW_B3.9610.07.05
DE_CW_B3.9610.07.05
BAL DE SD_Subdivision DE_CW_B3.9610.07.06
DE_CW_B3.9610.07.06
BAL DE SD_Subdivision DE_CW_B3.9610.07.07
DE_CW_B3.9610.07.07
BAL DE SD_Subdivision DE_CW_B3.9610.09.03
DE_CW_B3.9610.09.03
BAL DE SD_Subdivision DE_CW_B3.9610.09.04
DE_CW_B3.9610.09.04
BAL DE SD_Subdivision DE_CW_B3.9610.09.05
DE_CW_B3.9610.09.05
BAL DE SD_Subdivision DE_CW_B3.9610.09.06
DE_CW_B3.9610.09.06
BAL DE SD_Subdivision DE_CW_B3.9610.09.07
DE_CW_B3.9610.09.07
BAL DE SD_Subdivision DE_CW_B3.9610.09.08
DE_CW_B3.9610.09.08
BAL DE SD_Subdivision DE_CW_B3.9610.09.09
DE_CW_B3.9610.09.09
BAL DE SD_Subdivision DE_CW_B4.9610.07.08
DE_CW_B4.9610.07.08
BAL DE SD_Subdivision DE_CW_B4.9610.07.09
DE_CW_B4.9610.07.09
BAL DE SD_Subdivision DE_CW_B4.9610.09.10
DE_CW_B4.9610.09.10
BAL DE SD_Subdivision DE_CW_B4.9610.09.11
DE_CW_B4.9610.09.11
BAL DE SD_Subdivision DE_CW_B4.9610.09.12
DE_CW_B4.9610.09.12
BAL DE SD_Subdivision DE_CW_DEMV_OD_01
DE_CW_DEMV_OD_01
BAL DE SD_Subdivision DE_CW_DEMV_WP_01
DE_CW_DEMV_WP_01
BAL DE SD_Subdivision DE_CW_DEMV_WP_02
DE_CW_DEMV_WP_02
BAL DE SD_Subdivision DE_CW_DEMV_WP_03
DE_CW_DEMV_WP_03
BAL DE SD_Subdivision DE_CW_DEMV_WP_04
DE_CW_DEMV_WP_04
BAL DE SD_Subdivision DE_CW_DEMV_WP_05
DE_CW_DEMV_WP_05
BAL DE SD_Subdivision DE_CW_DEMV_WP_06
DE_CW_DEMV_WP_06
BAL DE SD_Subdivision DE_CW_DEMV_WP_07
DE_CW_DEMV_WP_07
BAL DE SD_Subdivision DE_CW_DEMV_WP_08
DE_CW_DEMV_WP_08
BAL DE SD_Subdivision DE_CW_DEMV_WP_09
DE_CW_DEMV_WP_09
BAL DE SD_Subdivision DE_CW_DEMV_WP_10
DE_CW_DEMV_WP_10
BAL DE SD_Subdivision DE_CW_DEMV_WP_11
DE_CW_DEMV_WP_11
BAL DE SD_Subdivision DE_CW_DEMV_WP_12
DE_CW_DEMV_WP_12
BAL DE SD_Subdivision DE_CW_DEMV_WP_13
DE_CW_DEMV_WP_13
BAL DE SD_Subdivision DE_CW_DEMV_WP_14
DE_CW_DEMV_WP_14
BAL DE SD_Subdivision DE_CW_DEMV_WP_15
DE_CW_DEMV_WP_15
BAL DE SD_Subdivision DE_CW_DEMV_WP_16
DE_CW_DEMV_WP_16
BAL DE SD_Subdivision DE_CW_DEMV_WP_17
DE_CW_DEMV_WP_17
BAL DE SD_Subdivision DE_CW_DEMV_WP_18
DE_CW_DEMV_WP_18
BAL DE SD_Subdivision DE_CW_DEMV_WP_19
DE_CW_DEMV_WP_19
BAL DE SD_Subdivision DE_CW_DEMV_WP_20
DE_CW_DEMV_WP_20
BAL DE SD_Subdivision DE_CW_DEMV_WP_21
DE_CW_DEMV_WP_21
Region/ subregion
BAL
Art. 8 countries involved
EE, DE, PL, LT, FI, DK, SE, RU, LV, ,
Art. 8 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" Intensive exchange of information: Development of joint assessment bases and joint assessment at the level of the Helsinki Commission (HELCOM) for the protection of the marine environment in the Baltic Sea area. At this level, integrated environmental assessments have repeatedly been carried out to create thematic assessment reports as the basis for the comprehensive assessment of the marine environment of the Baltic Sea (HELCOM HOLAS, 2010). The HOLAS report and the underlying assessment reports are the basis for the coordination of the national initial assessments at HELCOM level. The HOLAS report 2010 provides an overarching summary of the state of the marine environment in the Baltic Sea area. It is the starting point for the coordination of the initial assessment of the countries bordering the Baltic Sea and covers the four areas of nutrient inputs, hazardous substances, biodiversity and maritime shipping. There is also a chapter on costs and benefits. Based on the HOLAS report for the initial evaluations, the coherence in the area of ​​the regions is ensured. Separate bilateral agreements between the states concerned have taken place on individual sub-regions, so that further harmonization has also taken place in this area. In addition, intensive harmonization efforts are taking place within the framework of the HELCOM projects to develop a core indicator set (CORESET) and to review the ecological goals of the Baltic Sea Action Plan regarding eutrophication (TARGREV). In this context, HELCOM is currently developing core indicator sets with regard to biodiversity, hazardous substances and eutrophication. The economic and social analysis of the use of the Baltic Sea waters under German jurisdiction is uncharted territory. The necessary coordination with regard to the methodological approaches to be pursued took place across the EU within the framework of the CIS working group ESA. In addition to this multilateral coordination, trilateral coordination with DK and PL is currently being planned. It is known from the HELCOM cooperation that the results of the initial assessments are comparable.
Art. 8 regional coherence
Partial
Art. 8 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned (possibly regional) core indicator sets, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between HELCOM and EU procedures is also necessary.
Art. 9 countries involved
EE, DE, PL, LT, FI, DK, SE, RU, LV, ,
Art. 9 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" At HELCOM there was an intensive exchange about existing methods for describing the good condition as well as the coordination of their further development. As part of the HELCOM projects to develop a core set of indicators (CORESET) and to review the ecological goals of the Baltic Sea Action Plan with regard to eutrophication (TARGREV), core sets of indicators are being developed with regard to biodiversity, hazardous substances and eutrophication. These core indicators also contain goals or limits to determine when good environmental status has been achieved. At the time of reporting, the results from TARGREV are still the subject of national and regional discussions. Both projects were accompanied by a Joint Advisory Board (JAB) in which all member states were represented and to ensure that uniform principles are applied throughout the Baltic Sea. JAB also served as a platform for the exchange of national activities for the implementation of the Marine Strategy Framework Directive (MSFD) and has now been replaced by the group for the implementation of the ecosystem approach (GEAR). At the time of reporting, activities at HELCOM are ongoing to inventory the national approaches for the implementation of Articles 8, 9 and 10 MSFD and to assess the state of coordination. In addition to this multilateral coordination, trilateral coordination with DK and PL is currently being planned. In addition, details were also agreed in bilateral country meetings.
Art. 9 regional coherence
Partial
Art. 9 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned (possibly regional) core indicator sets, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between HELCOM and EU procedures is also necessary.
Art. 10 countries involved
EE, DE, PL, LT, FI, DK, SE, RU, LV, ,
Art. 10 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" At HELCOM there was an intensive exchange about existing methods for describing the good condition as well as the coordination of their further development. The basis for this is the HELCOM Baltic Sea Action Plan (BSAP), which was adopted in 2007. The Baltic Sea Action Plan deals with all major environmental problems that can affect the marine environment in the Baltic Sea and provides specific goals to counter them. The far-reaching campaigns build on the extensive and long-term cooperation within HELCOM. As part of the HELCOM projects to develop a core set of indicators (CORESET) and to review the ecological goals of the Baltic Sea Action Plan with regard to eutrophication (TARGREV), core sets of indicators are being developed with regard to biodiversity, hazardous substances and eutrophication. These core indicator sets also contain goals or limits to determine when good environmental status has been achieved. At the time of reporting, the results from TARGREV are still the subject of national and regional discussions. Both projects were accompanied by a Joint Advisory Board (JAB) in which all member states were represented and to ensure that uniform principles are applied throughout the Baltic Sea. JAB also served as a platform for the exchange of national activities for the implementation of the Marine Strategy Framework Directive (MSFD) and has now been replaced by the group for the implementation of the ecosystem approach (GEAR). At the time of reporting, activities at HELCOM are ongoing to inventory the national approaches for the implementation of Articles 8, 9 and 10 MSFD and to assess the state of coordination. In addition to this multilateral coordination, trilateral coordination with DK and POL is currently being planned. In addition, details were also agreed in bilateral country meetings. Coordination with CZ as a member state in the catchment area without marine waters takes place, as far as necessary, via the International Commission for the Protection of the Oder (IKSO).
Art. 10 regional coherence
Partial
Art. 10 regional coherence problems
The public participation is very long compared to other Member States at six months. As a result, DE (1) always has to complete its reports very early and then (2) only has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. The above-mentioned (possibly regional) core indicator sets, for example, could therefore not be taken into account in the current German Article 8-10 reports. In some areas, a comparison between HELCOM and EU procedures is also necessary.

Report type Member State report to Commission
MSFD Article Art. 3(1) Marine waters & Art. 4/2017 Decision: Marine regions, subregions, and subdivisions & Art. 5(2) & Art. 6 Regional cooperation
Member State Germany
Reported by Bundesministerium für Umwelt, Naturschutz und Reaktorsicherheit
Report date 2013-05-14
Report access ANSDE_MSFD4Geo_20121015.xml
Member state marine waters
DE
Region / subregion description
North-east Atlantic Ocean: Greater North Sea, incl. Kattegat & English Channel
Subdivisions
Germany has not reported any subdivisions for the North Sea.
MRUs description (AreaType)
The entire German part of the North Sea subregion is also the assessment area for all characteristics, targets and indicators. No further subdivisions were made for the 2012 reporting.
MRUs
Region or subregion Member state Area type Marine Reporting Unit MRU Name
ANS DE SR_Subregion DE_ANS
German part of the North Sea subregion
Region/ subregion
ANS
Art. 8 countries involved
DE, UK, DK, BE, SE, , NO, NL, , FR
Art. 8 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" Intensive exchange of information: Development of joint assessment bases and joint assessment at the level of the OSPAR Commission for the Protection of the Marine Environment of the Northeast Atlantic. At this level, integrated environmental assessments were repeatedly carried out to create thematic assessment reports as the basis for the OSPAR Quality Status Report (QSR) 2010. The QSR 2010 and the underlying assessment reports are the basis for the coordination of the national initial assessments at OSPAR level. The QSR provides an overarching summary of the environmental status of the north-east Atlantic and its five sub-regions including the North Sea. In this respect, it is proof of the coherence of the initial assessments at the level of the North Sea sub-region as well as the North-East Atlantic region. With regard to the national conclusions of the initial assessment, it was agreed that the parties concerned would coordinate at the sub-region level. The report on the ecological status of the Wadden Sea 2009 (QSR 2009). QSRs are regularly created by the trilateral Wadden Sea Cooperation between Denmark, the Netherlands and Germany (Trilateral Wadden Sea Cooperation, TWSC). OSPAR bodies have developed internal "Advice Documents", among other things for the development of assessment procedures and indicators. The Advice Documents for descriptors 1, 2, 4 and 6 together as well as for descriptors 5, 7, 8 and 10 are available on the CIRCA website. In these documents, all available information (national, EU) has been taken into account. For descriptors 1, 2, 4 and 6, the national approaches for assessment procedures within the framework of the Intersessional Correspondence Group on the Coordination of Biodiversity Assessment and Monitoring (ICG-COBAM) investigated and coordinated. This includes the development of a common set of regional core indicators. The economic and social analysis of the use of the North Sea waters under German jurisdiction is uncharted territory. The necessary coordination with regard to the methodological approaches to be pursued took place across the EU within the framework of the CIS working group ESA. In addition, a pilot study is currently taking place within the framework of OSPAR, which serves the purpose of further coordination. In addition to this multilateral coordination, bilateral coordination took place on October 11, 2011 with the UK and on November 25, 2011 with NL. Bilateral coordination with DK is currently being planned. The results of the initial assessments are comparable. However, the Wadden Sea is not considered by NL. Both UK and NL have longer experience of economic and social analysis. A first comparison with DK positions took place within the framework of a multilateral coordination carried out on 15 June 2012 in The Hague at the invitation of NL (BE, DE, DK, FR , UK, NL).
Art. 8 regional coherence
Partial
Art. 8 regional coherence problems
Public participation is very long compared to other Member States with six months. As a result, DE (1) must always finalise its reports very early and then (2) has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive (MSFD) makes coordination more difficult. For example, the above-mentioned regional core indicator set could not be taken into account in the current German Article 8-10 reports. in sub-areas, a reconciliation between OSPAR and EU procedures is also necessary.
Art. 9 countries involved
UK, DK, BE, SE, , NO, NL, , FR
Art. 9 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" The OSPAR contracting parties have intensively exchanged information about existing methods for describing good environmental status and coordinated their further development at OSPAR level. OSPAR bodies have internal "Advice Documents" for describing good environmental status and defining Goals and indicators developed. The Advice Documents for descriptors 1, 2, 4 and 6 together as well as for descriptors 5, 7, 8 and 10 are available on the CIRCA website. All available information (national, EU) has been taken into account in these documents. For descriptors 1, 2, 4 and 6, the national approaches for good environmental status within the framework of the Intersessional Correspondence Group on the Coordination of Biodiversity Assessment and Monitoring (ICG- COBAM) investigated and coordinated. This includes the development of a common regional core set of indicators. The descriptions of good environmental status were created at OSPAR level on the basis of an inventory of the national drafts for Articles 9 and 10 with regard to descriptors 3, 5, 7, 8, 9, 10 and 11 and jointly analyzed with regard to regional coherence. The evaluation ranged from good (D 5, 8, 9, 10) to adequate (D 3, 11) to poor (D 7) coordination. In order to improve regional coordination, a number of improvement measures to be implemented directly or after July 2012 were identified. In addition to this multilateral coordination, bilateral coordination took place on October 11, 2011 with GB and on November 25, 2011 with NL. A first comparison with DK positions took place within the framework of a multilateral coordination (BE, DE, DK, FR, GB, NL) carried out in The Hague on June 15, 2012 at the invitation of NL. In contrast to DE, UK and NL summarize GES and environmental objectives in one report or chapter, with NL also summarizing descriptors 1, 3, 4 and 6 as the descriptor "Marine Ecosystem".
Art. 9 regional coherence
Partial
Art. 9 regional coherence problems
Public participation is very long compared to other Member States with six months. As a result, DE (1) must always finalise its reports very early and then (2) has limited scope for coordination. In addition, the ambitious timetable of the MSFD makes coordination more difficult. For example, the above-mentioned (regional) core indicator sets could not be taken into account in the current German Article 8-10 reports. in sub-areas there is also a need for a reconciliation between HELCOM and EU procedures.
Art. 10 countries involved
IT, PL, UK, CZ, DK, AT, CH, BE, SE, , NO, NL, , FR, LU, LI
Art. 10 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" The OSPAR contracting parties have exchanged views on the development of coordinated environmental targets and indicators. The OSPAR bodies have developed internal "Advice Documents" to describe the good status and to define targets and indicators. The Advice Documents for descriptors 1, 2, 4 and 6 together as well as for descriptors 5, 7, 8 and 10 are available on the CIRCA website. All available information (national, EU) has been taken into account in these documents. Environmental targets were set at OSPAR level on the basis of an inventory of the national drafts for Articles 9 and 10 with regard to descriptors 3, 5, 7, 8, 9 , 10 and 11 were compared and jointly analyzed with regard to regional coherence. The evaluation ranged from good (D 5, 8, 9, 10) to adequate (D 3, 11) to poor (D 7) coordination. In order to improve regional coordination, a number of improvement measures to be implemented directly or after July 2012 were identified. For descriptors 1, 2, 4 and 6, the national approaches for the biodiversity targets and indicators within the framework of the intersessional correspondence group were on the Coordination of Biodiversity Assessment and Monitoring (ICG-COBAM) investigates and coordinates. This includes the development of a common set of regional core indicators. Further bases were the work of the trilateral Wadden Sea Cooperation between Denmark, the Netherlands and Germany (Trilateral Wadden Sea Cooperation, TWSC). In addition to this multilateral coordination, bilateral coordination took place on October 11, 2011 with the UK and on November 25th, 2011 with NL. A first comparison with DK positions took place as part of a multilateral coordination (BE, DE, DK, FR, UK, NL) carried out on June 15, 2012 in The Hague at the invitation of NL. In contrast to DE, UK and NL GES and environmental goals in one report or chapter, with NL additionally summarizing descriptors 1, 3, 4 and 6 as the descriptor "Marine Ecosystem". With regard to environmental objectives and indicators, DE follows a similar approach to the latter NL approach, but in which descriptors 1, 2, 4 and 6 are combined in one chapter. Coordination with (member) states in the catchment area without marine waters takes place where necessary , through the International Commissions for the Protection of the Elbe (IKSE) and the Rhine (IKSR).
Art. 10 regional coherence
Partial
Art. 10 regional coherence problems
Public participation is very long compared to other Member States with six months. As a result, DE (1) must always finalise its reports very early and then (2) has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. For example, the above-mentioned regional core indicator set could not be taken into account in the current German Article 8-10 reports. in sub-areas, a reconciliation between OSPAR and EU procedures is also necessary.

Report type Member State report to Commission
MSFD Article Art. 3(1) Marine waters & Art. 4/2017 Decision: Marine regions, subregions, and subdivisions & Art. 5(2) & Art. 6 Regional cooperation
Member State Germany
Reported by Bundesministerium für Umwelt, Naturschutz und Reaktorsicherheit
Report date 2013-05-14
Report access BALDE_MSFD4Geo_20121015.xml
Member state marine waters
DE
Region / subregion description
Baltic Sea
Subdivisions
Germany has not reported any subdivisions for the Baltic Sea.
MRUs description (AreaType)
The entire German part of the Baltic Sea region is also the assessment area for all characteristics, targets and indicators. No further subdivisions were made for the 2012 reporting.
MRUs
Region or subregion Member state Area type Marine Reporting Unit MRU Name
BAL DE RG_Region DE_BAL
German part of the Baltic Sea region
Region/ subregion
BAL
Art. 8 countries involved
EE, DE, PL, LT, FI, DK, SE, , RU, LV,
Art. 8 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" Intensive exchange of information: Development of common assessment bases and joint assessment at the level of the Helsinki Commission (HELCOM) for the protection of the marine environment in the Baltic Sea area. At this level, integrated environmental assessments have repeatedly been carried out to create thematic assessment reports as the basis for the comprehensive assessment of the marine environment of the Baltic Sea (HELCOM HOLAS, 2010). The HOLAS report and the underlying assessment reports are the basis for the coordination of the national initial assessments at HELCOM level. The HOLAS report 2010 provides an overarching summary of the state of the marine environment in the Baltic Sea area. It is the starting point for the coordination of the initial assessment of the countries bordering the Baltic Sea and covers the four areas of nutrient inputs, hazardous substances, biodiversity and maritime shipping. There is also a chapter on costs and benefits. Based on the HOLAS report for the initial evaluations, the coherence in the area of ​​the regions is ensured. Separate bilateral agreements between the states concerned have taken place on individual sub-regions, so that further harmonization has also taken place in this area. In addition, intensive harmonization efforts are being made within the framework of the HELCOM projects to develop a core indicator set (CORESET) and to review the ecological goals of the Baltic Sea Action Plan regarding eutrophication (TARGREV). In this context, HELCOM is currently developing core sets of indicators with regard to biodiversity, hazardous substances and eutrophication. The economic and social analysis of the use of the Baltic Sea waters under German jurisdiction is uncharted territory. The necessary coordination with regard to the methodological approaches to be pursued took place across the EU within the framework of the CIS working group ESA. In addition to this multilateral coordination, trilateral coordination with DK and PL is currently being planned. It is known from the HELCOM cooperation that the results of the initial assessments are comparable.
Art. 8 regional coherence
Partial
Art. 8 regional coherence problems
Public participation is very long compared to other Member States with six months. As a result, DE (1) must always finalise its reports very early and then (2) has limited scope for coordination. In addition, the ambitious timetable of the Marine Strategy Framework Directive makes coordination more difficult. For example, the above-mentioned (regional) core indicator sets could not be taken into account in the current German Article 8-10 reports. in sub-areas there is also a need for a reconciliation between HELCOM and EU procedures.
Art. 9 countries involved
EE, DE, PL, LT, FI, DK, SE, , RU, LV,
Art. 9 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" At HELCOM there was an intensive exchange about existing methods for describing the good status and the coordination of their further development. As part of the HELCOM projects to develop a core indicator set (CORESET) and to review the ecological goals of the Baltic Sea Action Plan with regard to eutrophication (TARGREV), core indicator sets are being developed with regard to biodiversity, hazardous substances and eutrophication. These core indicators also contain goals or limits to determine when good environmental status has been achieved. At the time of reporting, the results from TARGREV are still the subject of national and regional discussions. Both projects were accompanied by a Joint Advisory Board (JAB) in which all member states were represented and to ensure that uniform principles are applied throughout the Baltic Sea. JAB also served as a platform for the exchange of national activities for the implementation of the Marine Strategy Framework Directive (MSFD) and has now been replaced by the group for the implementation of the ecosystem approach (GEAR). At the time of reporting, activities are ongoing at HELCOM to inventory the national approaches to the implementation of Articles 8, 9 and 10 MSFD and to assess the state of coordination. In addition to this multilateral coordination, trilateral coordination with DK and PL is currently being planned. In addition, details were also agreed in bilateral country meetings.
Art. 9 regional coherence
Partial
Art. 9 regional coherence problems
Public participation is very long compared to other Member States with six months. As a result, DE (1) must always finalise its reports very early and then (2) has limited scope for coordination. In addition, the ambitious timetable of the MSFD makes coordination more difficult. For example, the above-mentioned (regional) core indicator sets could not be taken into account in the current German Article 8-10 reports. in sub-areas there is also a need for a reconciliation between HELCOM and EU procedures.
Art. 10 countries involved
EE, DE, PL, LT, FI, DK, SE, , RU, LV,
Art. 10 nature of coordination
DE as "co-lead" of the CIS working group GES has the joint development of the working basis "Common Understanding of (Initial) Assessment, Determination of Good Environmental Status (GES) & Establishment of Environmental Targets (Articles 8, 9 & 10 MSFD)" At HELCOM there was an intensive exchange about existing methods for describing the good status and the coordination of their further development. The basis for this is the HELCOM Baltic Sea Action Plan (? Baltic Sea Action Plan? BSAP?), Which was adopted in 2007. The Baltic Sea Action Plan addresses all major environmental problems that can affect the marine environment in the Baltic Sea and provides specific targets to address them. The far-reaching campaigns build on the extensive and long-term cooperation within HELCOM. As part of the HELCOM projects to develop a core indicator set (CORESET) and to review the ecological goals of the Baltic Sea Action Plan with regard to eutrophication (TARGREV), core indicator sets are being developed with regard to biodiversity, hazardous substances and eutrophication. These core indicator sets also contain goals or limits to determine when good environmental status has been achieved. At the time of reporting, the results from TARGREV are still the subject of national and regional discussions. Both projects were accompanied by a Joint Advisory Board (JAB) in which all member states were represented and to ensure that uniform principles are applied throughout the Baltic Sea. JAB also served as a platform for the exchange of national activities for the implementation of the Marine Strategy Framework Directive (MSFD) and has now been replaced by the group for the implementation of the ecosystem approach (GEAR). At the time of reporting, activities are ongoing at HELCOM to inventory the national approaches to the implementation of Articles 8, 9 and 10 MSFD and to assess the state of coordination. In addition to this multilateral coordination, trilateral coordination with DK and POL is currently being planned. In addition, details were also agreed in bilateral country meetings. Coordination with CZ as a member state in the catchment area without marine waters takes place, as far as necessary, via the International Commission for the Protection of the Oder (IKSO).
Art. 10 regional coherence
Partial
Art. 10 regional coherence problems
Public participation is very long compared to other Member States with six months. As a result, DE (1) must always finalise its reports very early and then (2) has limited scope for coordination. In addition, the ambitious timetable of the MSFD makes coordination more difficult. For example, the above-mentioned (regional) core indicator sets could not be taken into account in the current German Article 8-10 reports. in sub-areas there is also a need for a reconciliation between HELCOM and EU procedures.