important plant areas in central and eastern europe - Plantlife

important plant areas in central and eastern europe - Plantlife important plant areas in central and eastern europe - Plantlife

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Section 2 In eastern and south eastern Europe there were two main challenges in applying this criteria.The first was the process of translating EU and Bern classification systems into the national classification systems and further work needs to be carried out on this process in many countries.The second was the lack of habitat mapping data in most countries.The IPA process in these regions has also highlighted threatened habitats which are not currently recognised by the EU Habitats Directive or the Bern Convention and could be included in future revisions of the annexes of these legislative instruments. Data availability and data strategies There was a wide variety of data availability in the seven partner countries and the national IPA selection strategies reflect these data availability issues.This also had implications for how national teams prioritised the use of available resources between collating existing data and undertaking new fieldwork. In countries with a high level of recent, computerised and digitised plant and habitat records, much of the selection was based on existing data supplemented by fieldwork or specialist data collation for gap areas. In countries with a lower level of recent or computerised data the IPAs were identified using targeted fieldwork on potential sites, which were highlighted from the existing data. This project has also highlighted areas where we have no current data and these gaps will form the future of further IPA identification work. Site selection An IPA can be selected for one or more qualifying criteria.The basic principles of site selection, including guidelines on site boundaries, and criteria for selection, are given in the IPA Site Selection Manual. Each national team decided on their site selection strategy within the constraints of the criteria and thresholds. Fundamental to these national strategies were decisions of the number and size of IPAs and the definition of site boundaries. Each country decided on the balance of large IPAs with a mosaic of habitats and species and smaller IPAs identified to protect a particular species or habitat. Boundary demarcation, such as the treatment of small IPAs located near to each other, or the defining of boundaries in areas of fragmented habitats or land uses, was decided on the basis of the local conditions of ecological integrity, ownership and practical management. The size range of IPAs in the current project is as follows: up to 100 ha (281 IPAs), >100 and < 1000 ha (207 IPAs), >1000 and < 10,000 ha (148 IPAs), >10,000 and < 10,000 ha (111 IPAs) and > 100,000 ha (43 IPAs). Further work on direct conservation and site management on IPAs will also contribute to refining site selection and boundary definition guidelines for the future. Bryophytes, fungi, lichen and algae The IPA programme includes lower plants and fungi in the assessment methodology. These important organisms are neglected in existing nature conservation legislation and Europe has a particular global responsibility to conserve them. Bryophytes: mosses and liverworts, are well represented in this project.There were 54 bryophytes on the IPA list for the seven partner countries and they are recorded qualifying features on 77 IPAs. Bryophytes are also an important component of several of the threatened habitats under Criterion C and were also used in some countries as indicator species for assessing botanical richness under Criterion B. 18

Methodology Lichens There were 34 lichen species included in the IPA species list for the seven partner countries and they are qualifying features on 24 IPAs. The 1989 European Red List for Macro-lichens was used in this project, however this red list is now quite old and an updated European red list would certainly help to identify priority lichen species and sites. Lichens were also included in this project in some countries under Criterion B and under certain habitats in Criterion C. The availability of data was often a problem for this group. Fungi The list of 33 fungi species prepared by the European Committee for the Conservation of Fungi (ECCF) were included in the list for Criterion A. Fungi are recorded as qualifying features in 20 IPAs under Criterion A. There are significant differences in the specialist disciplines and in the conservation needs of plants and fungi, so in each country the mycologists made the decision on whether there was sufficient data and if it was appropriate to identify priority plant and fungi sites together or separately. Again it was also possible to identify sites for fungi conservation using Criterion B and Criterion C. In Estonia several sites were identified primarily for the importance of their fungi. Lack of data was a significant problem for fungi in this project.A European red list for fungi would help to identify priority species for conservation, and specific recognition for fungi in European legislation and policies would also help in their conservation. Algae Algae are poorly represented in the project, primarily because of the lack of data and the under-representation of algal species on national and regional conservation lists.The Bern Convention lists 12 algae species, although none of these occurred in the partner countries, and none are recognised in the EU Habitats Directive. However in Estonia, three sites have been proposed as IPAs entirely for their marine algae species, under Criterion B.A European red list for algae would also help to prioritise conservation action for this group. Methodology challenges: Putting theory into practice is always a challenging experience and much valuable information has been gained in the process of implementing the seven national projects and in other pilot projects.These experiences will be used to refine the methodology and prepare guidance information for new countries. The most common methodological challenges are: • Lack of recent and accessible data for species and habitats • Lack of red lists at the national and regional level • Deciding on the number and area of IPAs in each country • Defining practical boundaries Open methodological discussions among specialists, and transparency in site selection have been strong points of this project.The reasons for identifying sites as IPAs are made available to all, and with the rigorous selection of species and habitats under the criteria there can be no doubt about the importance of these sites. References Anderson, 2002 Identifying Important Plant Areas in Europe: A Site Selection Manual and a Guide to developing criteria in other parts of the world. Evans, S., Marren, P. & Harper, M., 2002, Important Fungus Areas: a provisional assessment of the best sites for fungi in the United Kingdom. Plantlife,Association of British Fungus Groups, British Mycological Society. Palmer, M., & Smart, J., 2001, Important Plant Areas in Europe: Guidelines for the Selection of Important Plant Areas in Europe. Planta Europa & Plantlife. Parmasto, E., Perini, C., & Rahko,T., 2004, Attempts to introduce fungi into nature conservation activities (Presentation: Planta Europa IV Conference,Valencia (www.nerium.net)) Plantlife International, 2003 Technical Report from 7 national IPA workshops in Central and Eastern Europe. (www.plantlife.org.uk) Plantlife International, 2003 Report from IPA CEE Regional Workshop in Bratislava, November 2003 (www.plantlife.org.uk) Planta Europa 1995, Proceedings of the First European Conference on the Conservation of Wild Plants, Hyères, France, 2-8 September 1995 (Ed. John Newton). Plantlife Planta Europa 1998, Second European Conference on the Conservation of Wild Plants, 9-14th June 1998, Uppsala, Sweden. (Ed. Hugh Synge & John Akeroyd) Swedish Threatened Species Unit & Plantlife Planta Europa 2001, Third European Conference on the Conservation of Wild Plants, 23-28 June 2001, Pruhonice, the Czech Republic: Developing a Plant Conservation Strategy for Europe. Czech Agency for Nature Conservation & Landscape Protection, Planta Europa, the Council of Europe. Stewart, N. F. 2004, Important Stonewort Areas, An assessment of the best areas for stoneworts in the United Kingdom. Plantlife International, Salisbury, U.K. 19

Section 2<br />

In <strong>eastern</strong> <strong>and</strong> south <strong>eastern</strong> Europe there were two ma<strong>in</strong> challenges <strong>in</strong> apply<strong>in</strong>g this<br />

criteria.The first was the process of translat<strong>in</strong>g EU <strong>and</strong> Bern classification systems <strong>in</strong>to<br />

the national classification systems <strong>and</strong> further work needs to be carried out on this<br />

process <strong>in</strong> many countries.The second was the lack of habitat mapp<strong>in</strong>g data <strong>in</strong> most<br />

countries.The IPA process <strong>in</strong> these regions has also highlighted threatened habitats which<br />

are not currently recognised by the EU Habitats Directive or the Bern Convention <strong>and</strong><br />

could be <strong>in</strong>cluded <strong>in</strong> future revisions of the annexes of these legislative <strong>in</strong>struments.<br />

Data availability <strong>and</strong> data strategies<br />

There was a wide variety of data availability <strong>in</strong> the seven partner countries <strong>and</strong> the<br />

national IPA selection strategies reflect these data availability issues.This also had<br />

implications for how national teams prioritised the use of available resources between<br />

collat<strong>in</strong>g exist<strong>in</strong>g data <strong>and</strong> undertak<strong>in</strong>g new fieldwork.<br />

In countries with a high level of recent, computerised <strong>and</strong> digitised <strong>plant</strong> <strong>and</strong> habitat<br />

records, much of the selection was based on exist<strong>in</strong>g data supplemented by fieldwork or<br />

specialist data collation for gap <strong>areas</strong>.<br />

In countries with a lower level of recent or computerised data the IPAs were identified<br />

us<strong>in</strong>g targeted fieldwork on potential sites, which were highlighted from the exist<strong>in</strong>g data.<br />

This project has also highlighted <strong>areas</strong> where we have no current data <strong>and</strong> these gaps<br />

will form the future of further IPA identification work.<br />

Site selection<br />

An IPA can be selected for one or more qualify<strong>in</strong>g criteria.The basic pr<strong>in</strong>ciples of site<br />

selection, <strong>in</strong>clud<strong>in</strong>g guidel<strong>in</strong>es on site boundaries, <strong>and</strong> criteria for selection, are given <strong>in</strong><br />

the IPA Site Selection Manual.<br />

Each national team decided on their site selection strategy with<strong>in</strong> the constra<strong>in</strong>ts of the<br />

criteria <strong>and</strong> thresholds. Fundamental to these national strategies were decisions of the<br />

number <strong>and</strong> size of IPAs <strong>and</strong> the def<strong>in</strong>ition of site boundaries. Each country decided on<br />

the balance of large IPAs with a mosaic of habitats <strong>and</strong> species <strong>and</strong> smaller IPAs<br />

identified to protect a particular species or habitat. Boundary demarcation, such as the<br />

treatment of small IPAs located near to each other, or the def<strong>in</strong><strong>in</strong>g of boundaries <strong>in</strong><br />

<strong>areas</strong> of fragmented habitats or l<strong>and</strong> uses, was decided on the basis of the local<br />

conditions of ecological <strong>in</strong>tegrity, ownership <strong>and</strong> practical management.<br />

The size range of IPAs <strong>in</strong> the current project is as follows: up to 100 ha (281 IPAs), >100<br />

<strong>and</strong> < 1000 ha (207 IPAs), >1000 <strong>and</strong> < 10,000 ha (148 IPAs), >10,000 <strong>and</strong> < 10,000 ha<br />

(111 IPAs) <strong>and</strong> > 100,000 ha (43 IPAs).<br />

Further work on direct conservation <strong>and</strong> site management on IPAs will also contribute<br />

to ref<strong>in</strong><strong>in</strong>g site selection <strong>and</strong> boundary def<strong>in</strong>ition guidel<strong>in</strong>es for the future.<br />

Bryophytes, fungi, lichen <strong>and</strong> algae<br />

The IPA programme <strong>in</strong>cludes lower <strong>plant</strong>s <strong>and</strong> fungi <strong>in</strong> the assessment methodology.<br />

These <strong>important</strong> organisms are neglected <strong>in</strong> exist<strong>in</strong>g nature conservation legislation <strong>and</strong><br />

Europe has a particular global responsibility to conserve them.<br />

Bryophytes: mosses <strong>and</strong> liverworts, are well represented <strong>in</strong> this project.There were 54<br />

bryophytes on the IPA list for the seven partner countries <strong>and</strong> they are recorded<br />

qualify<strong>in</strong>g features on 77 IPAs. Bryophytes are also an <strong>important</strong> component of several<br />

of the threatened habitats under Criterion C <strong>and</strong> were also used <strong>in</strong> some countries as<br />

<strong>in</strong>dicator species for assess<strong>in</strong>g botanical richness under Criterion B.<br />

18

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