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MSFD Article 8 Assessment of habitats David Connor European Commission, DG Environment Brussels Laurent Guerin Museum National d‘Histoire Naturelle Dinard, France MSFD Article 8 guidance workshop 20-21 April 2016, Brussels Relevant Descriptors: • Descriptor 1: Biodiversity • Biological diversity is maintained. The quality and occurrence of habitats and the distribution and abundance of species are in line with prevailing physiographic, geographic and climatic conditions. • Descriptor 6: Seafloor integrity • Sea-floor integrity is at a level that ensures that the structure and functions of the ecosystems are safeguarded and benthic ecosystems, in particular, are not adversely affected. • Worked example: NE Atlantic (OSPAR) Assessment framework Assessment of specific pressures and their impacts on ecosystem elements (Art. 8.1b) D2 D3 fishing D5 Assessment of ecosystem elements (Art. 8.1a) Bird groups (D1) Benthic broad habitats (D1, 6) D6 D7 loss D6 damage Pelagic broad habitats (D1) Reptiles (turtles) (D1) Mammal groups (D1) Fish groups (D1, 3) D8 D9 D10 D11 Other pressures Criteria for habitats in Decision proposal v2 • D1C5: The loss of extent of the habitat type, resulting from anthropogenic pressures, does not exceed 5% of the natural extent of the habitat in the assessment area. In cases where the loss exceeded this value in the reference year used for the Initial Assessment in 2012, there shall be no further loss of the habitat type. • D1C6: The spatial extent of impacts from anthropogenic pressures on the condition of the habitat, including its biotic (typical species composition and their relative abundance) and abiotic structure, and its functions, does not exceed 30% of its natural extent in the assessment area. Other relevant criteria: • • • • • • D2C3 (non-indigenous species) D3C1/2/3/4 (commercial fish) D5C6/7/8/9 (eutrophication) D6C2/3 (physical disturbance and loss) D7C2 (hydrographical changes) D8C2/4 (contaminants) Assessments of pressures for Article 8(1b) D6, D7 - Physical damage Physical loss Other D2C1 D3C1 D6C1 D6C1 D2C2 Assessments of state for Article 8(1a) D1C1 D1 D3 Species groups D1 Pelagic broad habitats D1C6 D1 D3 D6 Benthic broad habitats D1C5 D1C6 D1 D4 Ecosystems D1C2 D1C3 D1C4 D5C2 D5C3 D5C4 D5C5 D5C6 D5C7 D5C8 D6 Fishing/ by-catch D11C1 D11C2 D3 NIS D9C1 D10C1 D10C2 D2 D8C3 D11 D8C1 Sound, other energy D5C1 Litter S P D10 Secondary criterion Contaminants Nutrients Primary criterion D8, D9 D5 Decision outline D7C1 D3C2 D3C3 D3C4 D8C2 D8C4 D10C3 D8C2 D8C4 ? D2C3 D8C2 D8C4 ? D2C3 D3C2 D3C3 D6C2 D7C2 ? ? ? ? ? D2C3 ? ? D5C9 D4C1 D4C2 D4C3 D4C4 D5C3 D5C8 D5C2 ? • Assessment flow and methods of integration •D1/D6 •Benthic broad habitat types Broad habitat types – equated to EUNIS 2015/16 Hard Hard/soft Level 2 Biogenic Rock* habitat Coarse Mixed (flora/ fauna) Photic Soft Sand Other Mud e.g. nonoxygenbased habitats Littoral Infralittoral Aphotic Circalittoral Bathyal Abyssal *Includes soft rock, marls, clays, artificial hard substrata Proposed Broad Habitat Types •Scales/areas of assessment Defined set of (nested) areas Region Sub-region Sub-division National part of sub-division Coastal part (WFD) Habitat assessment areas – Greater North Sea D C E B A Assessment scenario - for a specified habitat and assessment area – multiple impacts - draw from other assessments Physical loss D6C3 loss (coastal infrastructure) Hydrological changes – impacts D7C2 D2C3 Hydrological changes – minor effects D5C8/9 D6C2 damage Physical damage (bottom trawling) impacts D7C2 Physical loss (offshore D6C3 loss infrastructure) Hydrological changes impacts Occasional disturbances - minor effects Greens – acceptable state Orange, red – unacceptable state D8C2 Adapted from OSPAR Biodiversity guidance for MSFD Benthic broad habitat (e.g. circalittoral sand) Both criteria to achieve threshold values Criterion D1C5 – habitat extent (proportion lost) Extent of physical loss – from D6C3 (loss) Criterion D1C6 – habitat condition (proportion impacted) Extent of physical damage – from D6C2 (damage) Subhabitat 1 Extent/distribution D1C5 Benthic condition D1C6 Threshold values for extent of loss and impact Extent of other impacts (e.g. D5 eutrophication, D8 contaminants) Subhabitat 2 Sub-habitats selected to assess condition Benthic condition D1C6 Threshold values for condition of sub-type Visualising the assessment results Possible ways to express extent to which GES is achieved: Proportion of habitats in GES/not in GES (total for assessment area) Possible ways to express extent to which GES is achieved: Proportion of habitats assessed in GES/not in GES for assessment area Worked example: OSPAR •D1 •Pelagic broad habitat types Broad Habitat Types Ecosystem component Benthic (formerly seabed) habitats Pelagic (formerly water column) habitats Habitat groups Littoral rock and biogenic reef Littoral sediment Infralittoral rock and biogenic reef Infralittoral coarse sediment Infralittoral sand Infralittoral mud Infralittoral mixed sediment Circalittoral rock and biogenic reef Circalittoral coarse sediment Circalittoral sand Circalittoral mud Circalittoral mixed sediment Upper bathyal rock and biogenic reef Upper bathyal sediment Lower bathyal rock and biogenic reef Lower bathyal sediment Abyssal rock and biogenic reef Abyssal sediment Variable salinity Coastal Shelf Oceanic D4 Bird group 1 Coastal Mammal group 1 Bird group 2 Bird group 3 Bird group 4 Shelf Ocean/deep sea Mammal group 2 Mammal group 3 D1 D1 D1 Pelagic habitats Turtles Fish group 1 Cephalopod group 1 Fish group 2 Fish group 3 Benthic habitats Cephalopod group 2 D1 Fish group 4 D1, D3 D1, 6 Key challenges and opportunities • Understanding current approaches between regions and countries • Making use of assessments from other descriptors (e.g. D5 eutrophication) • Agreeing appropriate scales of assessment (e.g. in Mediterranean and Black Sea) • Understanding level of detail needed for assessment and management purposes (degree of confidence) Concluding remarks and areas for further work • We are moving rapidly from conceptual to operational • Significant developments in past few years to: a. b. c. d. Map and model the seabed habitat types over all regions of Europe Map the different human activities and their (potential) pressures on the seabed Assess the distribution and extent of pressure per habitat type Use sensitivity assessments (generic) and ground-truth sampling (specific) to validate the outcomes of pressure/habitat overlays There is still need for discussion to reach consensus on a common approach, particularly integration of pressure/impact results with ‘state’ assessments and scales of assessment Plenty to discuss during the workshop!