Draft online platform (Fact sheet) 1. Habitat type code & name AA.E3Y Baltic photic shell gravel characterized by mixed infaunal macrocommunity in fine sandlike shell fragments Photo of habitat type Please upload 1 or 2 photos of the habitat type Photo description (describe habitat and location of the photo): There are no photos available for this biotope. Habitat definition A description of the habitat’s distribution, characteristic native biota, abiotic features, key ecological processes and interactions. Subheaders are: Description Characteristic species European Vegetation Checklist alliances (only for terrestrial types) Indicators of quality 1 Habitat description The biotope is encountered in the photic zone and is characterized by shell gravel covering more than 90% of the bottom, and most of the shell gravel having been ground down to sandlike fragments. Benthic macroinfauna species that occur in the biotope burrow down in to the substrate that is similar in structure to coarse sand. The community composition of macroinfauna is presumed to be different in the sand like shell gravel compared to coarser shell gravel consisting mainly of semi-intact shells among which many different animals can be found including non-burrowing animals. The interstitial space is smaller in the sand-like shell gravel substrate, enabling also burrowing polychaetes and amphipods to build tunnels using the small grains. The distribution of sand-like shell gravel bottoms in the Baltic Sea is unknown, only few small patches have been recorded from German waters. Increase in atmospheric CO2 leading to ocean acidification, eutrophication and pollution are seen as the major threats to the biotope. Ocean acidification is assumed to increase the rate by which the calcium carbonate of mollusc shells dissolve. It is however unclear in what way the process will affect the sand-like shell gravel. Due to a higher acidity, shell gravel may be ground down to a sand-like substrate at an increasing rate possibly making the sand like shell gravel more common, but the acidity may also increase the rate by which the grains are dissolved decreasing the sand-like shell gravel. Eutrophication affects the sand-like shell gravel biotope adversely by increasing the organic loading the Baltic Sea. The increasing organic load can lead to local oxygen depletion. Some of the sand-like shell gravel patches may also become covered by overgrowth of algae. Characteristic species Unknown Indicators of quality - Classification Please indicate equivalent classification types as relevant, including: EUNIS type Annex 1 type of the Habitats Directive IUCN Habitats Classification Scheme Emerald type Marine Strategy Framework Directive type EUSeaMap type European Forest Type MAES type (level 2) Other types... 2 Annex 1 relationships The relationship between HUB biotopes and Annex 1 habitats has not been mapped by HELCOM. MAES relationships Marine - Marine inlets and transitional waters Marine - Coastal MSFD relationships Shallow sublittoral coarse sediment Shallow sublittoral mixed sediment EUSeaMap relationships Shallow coarse or mixed sediments IUCN ecosystem relationships 9.3 Subtidal Loose Rock/Pebble/Gravel Other relationships EUNIS (2004) A5.113: Baltic shell gravel bottoms in the infralittoral photic zone. Level 5 of the HELCOM HUB (2013) classification. This habitat has no sub-habitats in the HELCOM HUB classification. Does the habitat type present an outstanding example of typical characteristics of one or more biogeographic regions? Please tick () one box only: (A habitat represents an outstanding example of typical characteristics of one or more biogeographical regions, if it is especially characteristic of one or more biogeographic regions, in terms of area, species composition, structure or functioning). YES : NO: UNKNOWN: If Yes – please indicate the regions For terrestrial types: Alpine Atlantic Black Sea Boreal Continental Macaronesia Mediterranean 3 Pannonian Steppic For marine types: Marine Atlantic Marine Baltic Marine Black Sea Marine Macaronesia Marine Mediterranean Justification: - 4 2. Geographic occurrence and trends Distribution map (in 10x10 km grids) of the habitat type in Europe (provided by Alterra/ NatureBureau) For both terrestrial and marine types, please tick () the countries in which the habitat type is present based on the territorial data sheets (please select “Present” or “Presence Uncertain” as relevant) EU 28 Austria Belgium Bulgaria Croatia Czech Republic Cyprus Denmark Estonia Finland Finland mainland Åland Islands France France mainland Corsica Germany Greece Greece (mainland and other islands) Crete East Aegean islands Hungary Ireland Italy Italy mainland Sardinia Sicily Latvia Lithuania Luxembourg Malta Netherlands Poland Portugal Portugal (mainland) Azores Madeira Savage Islands Romania Slovakia Slovenia Spain (mainland) Spain Balearic Islands Canary Islands Sweden United Great Britain 5 Kingdom Northern Ireland Gibraltar EU 28+ Albania Andorra Bosnia and Herzegovina Faroe Islands Guernsey Iceland Isle of Man Jersey Kaliningrad Kosovo Liechtenstein Former Yugoslavian Republic of Macedonia (FYROM) Monaco Montenegro Norway (mainland) Norway Svalbard Jan Mayen San Marino Serbia Switzerland Vatican City For marine habitats, please tick () the MSFD region and subregion in which the habitat type occurs (please select “Present” or “Presence Uncertain” as relevant): Mediterranean Sea Black Sea North-East Atlantic Baltic Sea Adriatic Sea Aegian-Levantine Sea Ionian Sea and the Central Mediterranean Sea Western Mediterranean Sea Black Sea Sea of Marmara Bay of Biscay and the Iberian Coast Celtic Seas Kattegat Greater North Sea Macaronesia Baltic Proper Belt Sea Gulf of Bothnia Gulf of Finland Gulf of Riga The Sound 6 Is the list of countries/seas selected above in correspondence with the provided map? Please tick () the box confirming that a consistency check has been done: For EU 28 and EU 28+: 1. Using the distribution map, the Project Management Team will provide the value for Extent of Occurrence (extent of a minimum convex polygon enclosing all occurrences) and for Area of Occupancy (number of 10*10 km cells occupied by the habitat type). 2. Using the territorial data sheets (along with additional information if relevant), please provide the estimated total area (actual area in km2 of the habitat), calculated by adding up the area of the habitat type in each country/sea. Extent of Occurrence (EOO) EU 28 EU 28+ Area of Occupancy (AOO) Current estimated Total Area (km2) Comments ≤ 55,000 km2 How much of the current distribution of the habitat type lies within the EU 28? Please estimate in percentage the proportion of the habitat type that the EU28 hosts in relation to the habitat type’s total worldwide distribution. For the marine types this is (by definition) compared to the total area within EU28+. In the Baltic Sea 100% of this habitat lies within EU 28. Trends in quantity Using the territorial data and any other relevant information, please describe the historical, recent and estimated future trends in quantity (extent, distribution). Current: The biotope occurs only in the south-western Baltic Sea, in the Belt Sea. EOO is ≤ 55,000 km2, but exact data on biotope decline is lacking. Past: The distribution of the habitat has declined due to degradation of the environmental quality caused by climate change and pollution. Historic: No data available. Future: No estimate available. 7 Average current trend in quantity (extent): EU 28 EU 28+ Stable Increasing Decreasing Unknown Stable Increasing Decreasing Unknown Does the habitat type have a small natural range following regression? Please tick () one box only: (The habitat has a small natural range following regression if the EOO ≤ 50,000 km² and the habitat has undergone an important decline during the last 50 years) YES : NO: UNKNOWN: Justification (please indicate whether the decline is ongoing or has stopped, and provide any additional supporting information): The distribution of sand-like shell gravel bottoms in the Baltic Sea is unknown, only a few small patches have been recorded from German waters. The distribution of the habitat has declined due to degradation of the environmental quality caused by climate change and pollution. Does the habitat have a small natural range by reason of its intrinsically restricted area? Please tick () one box only: (A habitat has a small natural range by reason of its intrinsically restricted area if the underlying factors for the occurrence of the habitat occupy a very limited area and range) YES : NO: UNKNOWN: Justification: See previous text box. 8 3. Habitat condition and trends Please describe the current quality of the habitat type, historical trends in quality and estimated future trends. Use and build on the information from the territorial data sheets and the quality indicators from the description. No information exists on the quality of the biotope. Average current trend in quality: EU 28 EU 28+ Stable Increasing Decreasing Unknown Stable Increasing Decreasing Unknown 4. Country/regional sea trends Using the territorial data sheets please indicate at the country or regional sea levels if the trends in quantity and quality are increasing, decreasing, stable or unknown. Current area of Recent trend in habitat (km2) quantity (last 50 yrs) Baltic Sea No data. Decreasing. Recent trends in quality (last 50 yrs) No data. Please upload all the territorial data sheets for this habitat type 9 5. Pressures and threats Indicate in the look-up table below (provided by Doug Evans and based on Article 17/MSFD) the five most significant threats affecting the habitat and whether these are of past, current or future importance. In the accompanying text field below, indicate the main causes of the threats affecting the habitat and their scale of significance within the EU 28 and EU 28+. Use and build on the information from the territorial data sheets and other available information. Past and Current Threats (Habitat directive article 17): Climate change (ocean acidification M01.04), Eutrophication (H01.05) Future Threats (Habitat directive article 17): Random threat factors (–), Climate change (ocean acidification M01.04), Eutrophication (H01.05) Increase in atmospheric CO2 leading to ocean acidification, eutrophication and pollution are seen as the major threats to the biotope. Ocean acidification is assumed to increase the dissolving rate of the calcium carbonate in mollusc shells. It is however unclear how the process will affect the sand-like shell gravel. Due to higher acidity, shell gravel may be ground down to a sand-like substrate at increasing rates possibly making the sand like shell gravel more common. On the other hand the increased acidity may also increase the dissolving rate of the grains thus decreasing the amount of sand-like shell gravel. Eutrophication affects the sand-like shell gravel biotope adversely by increasing the organic load in the Baltic Sea. The increasing organic load can lead to local oxygen depletion, and some of the sand-like shell gravel patches may also become covered by overgrowth of algae. 6. Conservation and management Please describe the main (e.g. no more than 5) current approaches to conservation and management of this habitat type, and outline what additional actions are needed. The extent and occurrence of the biotope needs to be mapped in more detail to establish whether the biotope also exists in areas outside the German exclusive economic zone. Conservation and management needs 10 Please tick the main essential and realistic conservation and management actions needed for the habitat type (following the description provided above). The actions should be selected only if they are relevant to the conservation of the particular habitat being assessed (the classification below is derived from the Habitats Directive Article 17 reporting) Code 1 1.1 1.2 1.3 Measure No measures needed for the conservation of the habitat/species Measures needed, but not implemented No measure known/ impossible to carry out specific measures 2 Measures related to agriculture and open habitats 2.0 2.1 Other agriculture‐related measures Maintaining grasslands and other open habitats 2.2 Adapting crop production 3 Measures related to forests and wooded habitats 3.0 3.1 Other forestry‐related measures Restoring/improving forest habitats 3.2 Adapt forest management 4 Measures related to wetland, freshwater and coastal habitats 4.0 4.1 4.2 Other wetland‐related measures Restoring/improving water quality Restoring/improving the hydrological regime 4.3 Managing water abstraction 4.4 Restoring coastal areas 5 Measures related to marine habitats 5.0 5.1 Examples No measures Other marine‐related measures Restoring marine habitats species migrations, habitat changes due to climate change, glacier retreat, monitoring changes without intervention mowing, burning, grazing, removal/control of shrubs and other woody plants adapting input of nutrients and pesticides/herbicides; adapting crop timing (advance/delay harvest dates) replanting with autochthonous species, enable/ promote natural re‐growth, removing non‐natives species, change single species and even‐aged stands into multi‐species and uneven‐aged stands, burning/ maintaining a fire regime adapting harvesting cycles, adapting techniques and equipment restoring alluvial situations, reducing eutrophication restoring river dynamics, removal of barriers and artificial margins, managing water levels (e.g. in bogs and mires) managing periods and/or quantity of water abstracted for irrigation, energy production stabilisation of dunes, re‐establishing dune dynamics, removing coastal infrastructures controlling invasive species, favouring re‐establishment of natural communities 11 6 Measures related to spatial planning 6.0 6.1 6.2 Other spatial measures Establish protected areas/sites Establishing wilderness areas/ allowing succession 6.3 Legal protection of habitats and species 6.4 Manage landscape features 6.5 Adaptation/ abolition of military land use 7 Measures related to hunting, taking and fishing and species management 7.0 7.1 Other species management measures Regulation/ Management of hunting and taking 7.2 Regulation/ Management of fishery in limnic systems 7.3 Regulation/ Management of fishery in marine and brackish systems Specific single species or species group management measures 7.4 8 regulation of hunting (periods, species), collection permits for plants, berries etc., regulation of game density regulation of amount, fish species & catching methods allowed, removal of certain fish species, control of measures for enhancing fish production, maintenance of traditional fish pond systems adapting fishing techniques and equipment, including mussel fishery management Measures related to urban areas, industry, energy and transport 8.0 8.1 8.2 Other measures Urban and industrial waste management Specific management of traffic and energy transport systems 8.3 Managing marine traffic 9 Measures related to special resource use 9.0 9.1 Other resource use measures Regulating/Management exploitation of natural resources on land Regulating/Managing exploitation of natural resources on sea 9.2 no intervention after calamities, natural catastrophic events, succession where no management is necessary legal habitat type protection (regardless where they occur, also outside protected areas), strictly legally protected species including their habitats maintenance or creation of hedges, tree lines, corridors nature management on military training grounds, abolition of military use measures to reduce collision, maintenance of semi natural roadsides, protection of birds on high voltage systems, regulations to manage traffic density managing routes, boat speed, management of quarries with amphibians, wind exploitation managing oil, gas, gravel/sand, wind exploitation on sea Conservation status Please indicate the overall conservation status in the relevant biogeographical regions of all related 12 Annex 1-types according to the Habitats Directive. For marine types, please also indicate the OSPAR or Helcom status if relevant. According to HELCOM Red List Assessment 2013 this habitat has been given the threat category NT according to criterion B1a (ii). When severely damaged, does the habitat retain the capacity to recover its typical character and functionality? Estimate the time taken for such recovery (1) naturally and (2) through intervention. Please fill in the matrix below. Justification (please also describe the specific resources and actions required to recover the habitat, if possible): Time (years) None Low Effort required Medium High 10 yrs 20 yrs 50+ yrs 200+ years 7. Synopsis Please synthesize the relevant information obtained from the territorial data sheets and other sources in order to facilitate the assessment process. Input data: - HELCOM Red List of Biotopes Questionnaire raw data - Expert judgement - Subsequent expert discussions in the HELCOM Red List of Biotopes assessment - HELCOM Biotope Information Sheet for the habitat AA.E3Y Baltic photic shell gravel characterized by mixed infaunal macrocommunity in fine sand-like shell fragments 13 8. Red List assessment Criterion A: Reduction in quantity Please indicate in the table below the percentage of decline obtained after applying Criterion A, as far as data are available. Explain the percentage and provide any supporting evidence, including the map base or other source(s) used to estimate change in distribution. If A2b was applied, please also give the beginning and end (in years) of the 50-year period over which the decline was measured. Please cite data sets and other sources of information used; if the primary data has not been published, please provide a copy for archive to support future re-assessments. Criterion A EU 28 EU 28+ A1 No data available No data available A2a No data available No data available A2b No data available No data available A3 No data available No data available Criterion B: Restricted geographic distribution Please indicate in the table below the values obtained after applying Criterion B, as far as data are available. Explain the values and provide any supporting evidence. If B1a or B2a is used, please indicate which subcriteria (i, ii and/or iii) this is based on. If B1b or B2b is used, please explain the threatening processes and their effects. If B3 is used, please give the most serious plausible threat and justify how it will cause the habitat to become Critically Endangered or Collapsed, including the time frame in which this could occur. Please cite data sets and other sources of information used; if the primary data has not been published, please provide a copy for archive to support future re-assessments. Criterion B B1 EOO a EU 28 ≤ 55,000 km2 ii EU 28+ No data available B2 b c AOO No data available No data available a b c B3 No data available No data available The distribution of sand-like shell gravel bottoms in the Baltic Sea is unknown, only a few small patches have been recorded from German waters. The Extent of occurrence of the biotope is estimated to be ≤ 55 000 km2, but exact data on biotope decline is lacking. The distribution of the habitat has however declined due to degradation of the environmental quality caused by climate change and pollution. 14 Criteria C and D: Reduction in abiotic and/or biotic quality Please indicate in the table below the percentage of change in abiotic and/or biotic quality. Please report them together (criterion C/D), but if possible, also report abiotic (criterion C) and biotic (criterion D) percentages separately. Please explain the resulting values obtained, and provide any supporting evidence. Whenever possible, please identify the abiotic environmental and/or biotic ecological factor(s) and data sources used to assess reduction in quality. If criteria C/D2, C2 or D2 are used, please define the 50-year time period over which the reduction was measured. Please cite data sets and other sources of information used; if the primary data has not been published, please provide a copy for archive to support future reassessments. C/D1 Criteria C/D EU 28 EU 28+ Criterion C EU 28 EU 28+ Criterion D EU 28 EU 28+ Extent affected (%) No data available No data available Relative severity No data available No data available C1 Relative Extent severity affected (%) (%) No data No data available available No data No data available available D1 Relative Extent severity affected (%) (%) No data No data available available No data No data available available C/D2 Extent Relative affected severity (%) No data No data available available No data No data available available C2 Extent Relative affected severity (%) (%) No data No data available available No data No data available available D2 Extent Relative affected severity (%) (%) No data No data available available No data No data available available C/D3 Extent affected (%) No data available No data available Extent affected (%) No data available No data available Extent affected (%) No data available No data available Relative severity No data available No data available C3 Relative severity (%) No data available No data available D3 Relative severity (%) No data available No data available 15 Criterion E: Quantitative analysis to evaluate risk of habitat collapse Describe the method/model used to estimate risks of habitat collapse. Please explain the resulting values obtained, specify the basis and provide any supporting evidence. Please cite data sets and other sources of information used; if the primary data has not been published, please provide a copy for archive to support future re-assessments. Criterion E EU 28 EU 28+ E No data available No data available No quantitative analysis has been carried out for this habitat. Overall assessment “Balance sheet” for EU 28 and EU 28+ 1 Please complete the table below, indicating the Red List Category that the habitat type qualifies for, after assessing the habitat types against all criteria for which data is available. If any criteria were not applied, the habitat type should be considered Data Deficient (DD) under those criteria. Category EU 28 EU 28+ A1 DD DD A2a DD DD A2b DD DD A3 DD DD Category EU 28 Category EU 28+ EU 28 Category EU 28+ EU 28 Category EU 28+ EU 28 Category EU 28+ B1 NT NT C/D1 DD DD C1 DD DD D1 DD DD B2 DD DD C/D2 DD DD C2 DD DD D2 DD DD B3 DD DD C/D3 DD DD C3 DD DD D3 DD DD EU 28 E DD Overall Category & Criteria EU 28+ DD EU 28 NT B1a (ii) Synthesis Provide a summary of the reasons why the habitat type qualifies for the Category and Criteria recorded above, justifying assessment decisions, limits of data quality, reliability of assessment, etc.), using the information from above. The distribution of sand-like shell gravel bottoms in the Baltic Sea is unknown, only a few small patches have been recorded from German waters. The Extent of occurrence of the biotope is estimated to be ≤ 55 000 km2, but exact data on biotope decline is lacking. The distribution of the habitat has however declined due to degradation of the environmental quality caused by climate change and pollution. 1 This table possibly will be filled automatically in the online platform 16 EU 28+ NT B1a (ii) Please indicate the confidence in the assessment; please tick () one box only: Low (mainly based on uncertain or indirect information, inferred and suspected data values, and/or limited expert knowledge) Medium (evenly split between quantitative data/literature and uncertain data sources and assured expert knowledge) High (mainly based on quantitative data sources and/or scientific literature) Sub-habitat types that may require further examination Indicate and specify if any sub-types of the assessed habitat type which may require further examination due to their particular character or potentially threatened status. These may be subtypes in a specific region, or thematic subtypes, having a certain specific species composition or structure. This biotope has no further sub-biotopes according to current classification (HELCOM HUB 2003). Assessors Please indicate the names of the individuals that have assessed the status of the habitat type (the working group members, first name is the member tasked to write up the draft assessment). HELCOM RED LIST Biotope Expert Team 2013 and Baltic Sea Working Group for the European Red List of Habitats 2014. Contributors Please indicate the names of the individuals that have contribute to the assessments (including providers of territorial data, and providers of descriptions of types, and any other contributors). HELCOM RED LIST Biotope Expert Team, November 2013. Reviewers Please indicate the names of the individuals that have reviewed the assessment. Dates of the assessment Please indicate the date when the habitat type was assessed (WG assessment workshop and/or synthesis workshop if changes are made in a later stage). November 2013. Date of review Please indicate the date when the habitat type assessment was peer-reviewed. 17 9. References Provide a list of all published and unpublished reference sources used for the information recorded above, including data sets and other sources of information. If the primary data has not been published, please provide a copy for archive to support future re-assessments. Please provide full references, and try to avoid abbreviations (e.g. write Conservation Biology rather than Cons. Biol.). HELCOM 2013. Red List of Baltic Sea underwater biotopes, habitats and biotope complexes. Baltic Sea Environmental Proceedings No. 138. 18