Strasbourg, 14 February 2006 T-PVS/Emerald (2006) 1
[T-PVS/Emerald01e_06 ] English only
CONVENTION ON THE conservation of EUROPEAN wildlife
and natural habitats
Group of Experts for the setting up
of the Emerald Network of Areas of Special Conservation Interest
---ooOoo---
Emerald Network Pilot Project in Serbia and Montenegro
- Report-
Document established by
the Malta Environment & Planning Authority
Prepared by Ana Pajević
Ministry of environmental protection and physical planning
Podgorica, Montenegro
December, 2005
TABLE OF CONTEST
- Background
- Emerald Network in Serbia and Montenegro
- Emerald Network project team
- List of Emerald team
- Activities carry out in a framework of pilot project
- List of endangered natural habitats requiring specific conservation measures in Serbia and Montenegro (Resolution No 4 (1996))
- List of species requiring specific habitat conservation measures in Serbia and Montenegro (Resolution No. 6 (1998) of the Standing Committee
- List of biogeographical zones in country
- Selection of potential Areas of Special Conservation Interest (ASCI)
- Problems and solutions
- Follow up activities
- Proposal for expansion of Emerald species list
- Annex 1. List of endangered natural habitats requiring specific conservation measures in Serbia and Montenegro (Resolution No. 4 (1996)
- Annex 2. List of species requiring specific habitat conservation measures in Serbia and Montenegro (Resolution No. 6 (1998) of the Standing Committee
- Annex 3. Maps of selected site in Serbia and Montenegro
- Annex 4. Proposal for expansion of Emerald species list
- Annex 5. Workplan of project acitivities
Background
The territory of Serbia and Montenegro (SCG), with an area of 102,173 km2, makes only 0.07% of the entire world’s land, and 2.1% of the European continent. Along a 600 km horizontal transect, from the Montenegrin coast in the southwest through Pannonian Plain (Vojvodina) in the north, and along the vertical transect in the mountains of Serbia and Montenegro, segments/equivalents of almost all major European zonobiomes are represented (Mediterranean evergreen forests along the Adriatic coast, sub-Mediterranean mixed-deciduous forests and scrubs in Mediterranean hinterlands, deciduous forests in lowland, hilly and montane zones, boreal-type forests in subalpine belts, steppes and forest-steppes in Vojvodina; also, the high-alpine and oro-Mediterranean "oro-biomes" above the timber line in high-montane regions). In more generalized respect, 5 out of the 12 principal terrestrial biomes of the world may be distinguished, and the complex of marine biota may be regarded as the sixth biome.
Serbia and Montenegro may be divided into four distinct geographical/orographic entities:
§ Northern lowland part, belonging to the Pannonian Plain;
§ Central part – mountains, hills and valleys of the Balkan mainland; and
§ Adriatic coast in Montenegro;
§ Adriatic Sea.
Biogeographically, the territory of Serbia and Montenegro may be divided into the five regions (Mediterranean, Central European, Pontic-Southsiberian, Circum-boreal and Central-South-European montane regions), 8 subregions and 20 provinces (STEVANOVIĆ, 1995).
It is situated between three principal eco-climatic regions of Europe: northern (boreal and temperate), eastern (Pontic) and southern (Mediterranean). General biogeographical characteristics are locally modified and diversified by varied orographic and petrographic composition of the territory, as well as by complex history of the flora and fauna, during the late Tertiary and Pleistocene, resulting in the complex composition of the biota and ecosystems, and their mosaic distribution. The territory of Serbia and Montenegro encompasses some of the most important Ice Age refuge regions of Europe. Southern location of Yugoslav territorial waters, within the Adriatic Sea Basin, accounts for the relatively great diversity of marine biota.
Being located in the central part of the Balkan Peninsula bordering south-eastern Pannonian Plain, at the crossroads of varying biogeographical impacts and routes, the biota in Serbia and Montenegro are, generally, very rich and varied, relative to the other countries and regions in Europe of comparable size. As usual, when such large and diversified segments of biota are considered, the availability of the basic information on the floristic/faunal composition, distribution, basic taxonomy, etc. is quite heterogeneous, hence the reliability of diverse conclusions is also variable.
Serbia and Montenegro is among the floristically most diverse parts of the Balkan Peninsula, comparable only to Greece and Bulgaria. According to the international criteria of IUCN-WMC, the territory of FR Serbia and Montenegro, together with the mountainous area of Bulgaria, represents one of the six European and one of the 153 world’s centres of floristic diversity. Within its territory, 44.28% of the native mosses and 38.93% of the vascular plants of Europe are found; it comprises about 60% of plant species in the flora of the Balkan Peninsula (7,500).
According to the most recent estimates, flora of Serbia and Montenegro comprises around 1,400 species of freshwater algae, 1,500 species of marine algae, 565 species of mosses, and 4,182 taxa (3,905 species and 277 subspecies, classified in 888 genera and 157 families) of vascular plants, which places Serbia and Montenegro among European countries with the greatest floristic diversity and density per unit area (Tab. 1). The extraordinary taxonomical richness of the Yugoslav vascular flora is obvious in comparison with that of the whole of Europe, which comprises some 11,000 species, in 1,541 genera and 203 families. In addition to the plants, some 516 species of lichens are recorded, and the mycoflora includes around 1,000 recorded species of macromycetes (the latter estimated at 3,500-4,500 species).
The share of endemic, endemo-relict and relict plants greatly contribute to the richness and diversity of the flora of Serbia and Montenegro, being specific and different from other parts of Europe. The number of Balkan endemics in Serbia and Montenegro is particularly great, amounting to 392 taxa (species or subspecies), which accounts for 9.15% of the flora of Serbia and Montenegro.
The predominant kind of endemism in Serbia and Montenegro, as well as in the Balkans generally, is the high-mountain one. The greatest diversity centres of endemic flora are mainly high mountains, such as Prokletije, Šar-Planina, Koritnik, Paštrik, Kopaonik, Stara Planina and Suva Planina, with 31-90 endemic species recorded per 100 sq km (UTM 10 x 10 km). In addition to high-mountain endemism, the edaphic endemism i.e. that related to particular bedrock is also great. Of special interest are serpentine habitats, particularly in W. and C. Serbia and Metohia, inhabited with ophiolitic endemic flora.
Of particular global significance and great scientific interest are endemics restricted to the territory of Serbia and Montenegro – the local endemics; there are 87 locally endemic plants, that makes ca 2% of the total vascular flora of Serbia and Montenegro, or 22% of the total endemic flora of Serbia and Montenegro. Particularly large number of locally endemic plants inhabit the mountains of Prokletije and Šar-Planina. Among local endemics, of particular significance are those belonging to endemic Balkan genera, like: Pancicia (P. serbica), Protoedraianthus (P. tarae), Petteria (P. rhamentacea), Halascya (H. sendtneri), Amphoricarpus (A. neumayeri, A. autariatus, A. bertisceus); also, some subendemic genera are also very important, particularly Ramonda (R. serbica, R. nathaliae) and Edraianthus (ca. 20 Balkan endemics).
Local endemics are mostly of Tertiary origin (paleostenoendemics, endemo-relicts). Generally, relicts in the vascular flora of Serbia and Montenegro are of particular importance as potential genetical resources. These ancient plants are principally distributed in southern areas, scattered throughout the Mediterranean, but in only a few other parts of Europe. In Serbia and Montenegro they occupy specific habitats, primarily canyons, gorges and mountain tops, as well as the remaining enclaves of steppe regions in Vojvodina. According to their age of origin, the relicts are classified into Tertiary, glacial, boreal, and xerothermal elements.
The basic knowledge about the diversity of many animal taxa, and in particular, about the status of threat, is rather scanty, with the exception of a limited number of groups – principally the vertebrates, butterflies, and a few others (Tab. 2).
The estimated number of insects (>37,000) is certainly among the highest in Europe, but these numbers can not be appropriately verified (except for the best studied groups and some general numeric regularities); nevertheless, entomofauna comprise as much as 30 (out of about 35 known) insect orders and over 70% of known insect families. The number of the so far examined non-insect invertebrates is estimated to be approximately 15,000. About 465 fish (Chondrichthyes and Osteicthyes) and lampreys (Cephalaspidomorpha) species were recorded in the waters of Serbia and Montenegro, of which some 115 species live in freshwaters and more than 405 in the Adriatic Sea. There are 70 species of amphibians and reptiles, 382 species of birds and 96 species of terrestrial mammals that were also recorded within the territory of Serbia and Montenegro.
Out of stated 382 species of birds, which are either regularly, occasionally or potentially present in Serbia and Montenegro, the number of regularly occurring species is 333, of which there are 260 species of breeding birds; comparing this parameter, as most relevant for biodiversity assessments, with the total of 300 species of breeding birds in the whole of the Balkan Peninsula, we may conclude that Serbia and Montenegro supports 87% of Balkan diversity, the percentage which is much higher than in many other countries. Similarly, we may establish that Serbia and Montenegro harbours 51.16% of the European fish fauna, 74.03% of the European birds and 67.61% of the European mammals. The percentage for the amphibians and reptiles (combined) is somewhat less remarkable – 25.27%, but this is largely due to the extremely great faunistic riches of some small periphery areas of Europe; otherwise, just a few individual countries have the number of taxa similar to Serbia and Montenegro (Italy and Greece – 74 species each, Spain – 66).
Emerald Network in Serbia and Montenegro
A Pilot Project was launched in January 2005 in order to start the implementation of the Emerald Network in Serbia and Montenegro, under the responsibility of the Ministry of Environment and Physical Planning Republic of Montenegro.
Serbia and Montenegro is in the process of ratification of the Bern Convention and has taken fully into consideration the provisions of the Convention and in particular Recommendation No. 16 (1989) and Resolution No. 3 (1996). The Emerald Pilot Project is intended to serve as a ground for accelerating the process of accession of Serbia and Montenegro to the Bern Convention and can be used to define more areas of national importance for nature conservation.
Emerald Network project team
The national Emerald network team was formed after signing the project contract. The team consists of 28 experts. The team was mainly based on capacity from Institute for nature protection, University of natural sciences and Natural history museum from both republics. The project team leader and technical expert is representative of the Ministries of Environment, which is responsible for project implementation.
List of Emerald team:
Republic of Montenegro
Republic of Serbia
Activities carry out in a framework of pilot project
The Emerald Workshop
The workshop was held on 26-27 April 2005 in Podgorica, Republic of Montenegro in order to introduce the national team to the principle and technical aspects of the Emerald network and organize training for the team. The session was managed by working presidency: Ms.Ana Pajevic, project manager for the Emerald network in S&M, Mr. Eladio Fernandez Galiano and Mr. Mark Roekaerts from the Council of Europe.
Mr. Eladio Fernandez Galiano presented a hole activities of the Council of Europe and explained the legal framework of the Emerald network and the criteria for selection of ASCI and introduced the following relevant Emerald documentation.
Mr. Mark Roekaerts, expert for Emerald software presented the final version of the Emerald network software and explained step by step the introduction of data into the software by interactive work on a specific task.
Also, a representative from the Ministry of science and environmental protection, Republic of Serbia and a representative from the Institute for nature protection, Republic of Montenegro gave a detailed overview of biodiversity conditions and the legislative framework in respective republics.
The software was installed both in the Institute for nature protection in the Republic of Montenegro and in the Institute for nature protection in the Republic of Serbia.
In Serbia and Montenegro, several laws regulate nature protection on a republican level, such as the Environment Law, Law on Nature Protection, Law on coastal zones, the Law on National Parks and the Directive on protection of natural rarities.
There are no overall strategic documents on biodiversity management or a policy in terms of nature conservation.
There are 5 national parks in Serbia[1], and 4 national parks in Montenegro and larger number of protected areas.
A total of 8.836.100 ha or 5.93% of the Serbian territory is under protection regime ( 5 national parks, 72 nature reserves, 13 natural parks, 31 cultural and historical important areas, 13 landscape and 256 monuments of nature). The Landscape Spatial Plane of the Republic of Serbia (1996) projects planned to protect 10% of the territory by the year 2010. In Serbia national legislation currently provides for the protection of 215 plant and 427 animal species.
A total of 98,570 ha or 7.14% of the Montenegrins territory is under protection regime (4 national park, 4 reserves of nature and 51 monuments of nature). The most important natural resources in Montenegro are 4 national parks. In Montenegro national legislation currently provides for the protection of 314 animal and 57 plant species.
A number of nature areas have been recognized as internationally significant. Among these are the Obed Swamps and the Ludas Lake, Skadar Lake and Carska bara - Stari Begej and Slano Kopovo (Ramsar Wetland of International Significance). Others include the Durmitor-National Park, which includes part of the Tara River Canyon and the Kotor-Risan-Bay (a World Natural Heritage site), the Tara River Basin (UNESCO-MAB) and the Golija Biosphere Reserve (UNESCO MAB).
Protected Areas (PA), at present in Montenegro
(i) PAs by national legislature
Name and national category of the PAs |
IUCN mangm category |
Area (hectares) |
Percentage of the State territry (13.812 km2) |
National parks |
II |
83.000 |
6,01% |
Skadar lake |
II |
40.000 |
|
Lovćen |
II |
6.400 |
|
Durmitor |
II |
31.200 |
|
Biogradska gora |
II |
5.400 |
|
Nature monuments |
III / V |
7.733 |
0.6% |
Gorge Đalovića |
III / V |
1.600 |
|
Cave Lipska |
III / V |
/ |
|
Cave Magara |
III / V |
/ |
|
Cave Globočica |
III / V |
/ |
|
Cave near to Trnovo / Virpazar |
III / V |
/ |
|
Cave Babatuša |
III / V |
/ |
|
Cave Novakovića near to Tomaševo |
III / V |
/ |
|
Pothole Duboki do in Njegušima |
III / V |
/ |
|
Canyon of Piva river (downstream of the dam Mratinje) |
III / V |
1.700 |
|
Canyon of Komarnica river |
III / V |
2.300 |
|
Association of Pinetum mughi montenegrinum located at Ljubišnja (1.000ha) , Durmitor (5.200ha) and Bjelasica (400ha) |
III / V |
1.000 |
|
Association of Pinus heldraichii) located at Orjen (300ha), Lovćen (300ha) and Rumija (100ha) |
III / V |
400 |
|
Beaches at the Skadar lake shore |
III / V |
/ |
|
Beach Velika Ulcinjska |
III / V |
600 |
|
Beach Mala Ulcinjska |
III / V |
1,5 |
|
Beach Valdanos |
III / V |
3 |
|
Beach Velji pijesak |
III / V |
0,5 |
|
Beach Topolica, Bar |
III / V |
2 |
|
Beach Sutomore |
III / V |
4 |
|
Beach Lučica, Petrovac |
III / V |
0,9 |
|
Beach Čanj |
III / V |
3,5 |
|
Beach Pećin |
III / V |
1,5 |
|
Beach Buljarica |
III / V |
4 |
|
Petrovačka Beach |
III / V |
1,5 |
|
Beach Drobni pijesak |
III / V |
1 |
|
Beach Sveti Stefan |
III / V |
4 |
|
Beach Miločer |
III / V |
1 |
|
Becicka Beach |
III / V |
5 |
|
Beach Slovenska, Budva |
III / V |
4 |
|
Beach Mogren |
III / V |
2 |
|
Beach Jaz |
III / V |
4 |
|
Beach Pržno |
III / V |
2 |
|
Hill Savinska Dubrava in Herceg Novi |
III / V |
35,46 |
|
Botanical reserve of laurel and oleandera above the spring Sopot near to Risan |
III / V |
40 |
|
Botanical garden of the mountain flora in Kolašin |
III / V |
0,64 |
|
Botanical garden of general Kovačević in Grahovo |
III / V |
0,93 |
|
Park “13 jul”, and “Njegošev park” in Cetinje |
III / V |
7,83 |
|
Park near to hotel Boka in Herceg Novi |
III / V |
1,2 |
|
City park in Tivat |
III / V |
3 |
|
Park of the Castle at Topolica |
III / V |
2 |
|
Areas of Exeptional Natural Values |
III |
322,5 |
0,02% |
Hill Spas above Budva |
III |
131 |
|
Cape Ratac with Žukotrljica |
III |
30 |
|
Island Stari Ulcinj |
III |
2,5 |
|
Hill Trebjesa, Nikšić |
III |
159 |
|
Other PAs – protected by municipality regulations |
III |
15.000 |
1.08% |
Kotor – Risan bay, Municipality Kotor |
III |
15.000 |
|
Nature Reserves |
I |
500 |
0.03% |
- In NP Skadar lake: Manastirska tapija, Pančeva oka, Crni žar, Grmožur i Omerova gorica |
I |
420 |
|
- In NP Durmitor: Crna Poda |
I |
80 |
|
In TOTAL, under national protection |
106.655 |
7.72% |
Protected Areas by international legislature
Name and internationa categoty of the PAs |
Area (hectares) |
Percentage of the State territry (13.812 km2) |
a) Tare River basin – The World Biosphere Reserve - M&B, UNESCO including b) NP Durmitor with canyon of Tara River, protected as World Heritage site – UNESCO(natural) |
182.899 |
|
Kotor-Risani bay - World Heritage site – UNESCO (cultural) including Town Kotor as an endangered World Heritage site |
15.000 |
|
Skadar lake – Ramsar site (area of the Nacionalni Park) |
40.000 |
|
In TOTAL, under international protection |
237.899 |
17,2% |
Planned[2] Protected Areas
Protected area |
IUCN mngm. categor. |
Area (hectares) |
Percentage of State territory (13.812 km2) |
National Parks |
II |
14.000 |
|
Prokletije |
II |
14.000 |
|
Regional Parks |
III |
124.200 |
|
Orjen mt. |
III |
19.000 |
|
Rumija mt. |
III |
12.200 |
|
Komovi mt. |
III |
21.000 |
|
Sinjajevina mt with Šaranci |
III |
42.400 |
|
Maglic, Bioc & Volujak mts |
III |
7.200 |
|
Ljubišnja mt. |
III |
7.800 |
|
Turjak mt and Hajla mt |
III |
14.600 |
|
Natural monuments |
III (alt V)Š1Ć |
>2.000 (č5.800) |
|
Platije – middle part of Canyon Moraca River |
III |
Has not been defined, yet |
|
Cijevna river Canyon up to village Dinosa |
III |
2.000 |
|
Mala Rijeka River Canyon |
III |
Has not been defined, yetŠ2Ć |
|
Protected Landscapes |
III |
117.300 |
|
Visitor & Zeletin mts |
III |
31.000 |
|
Beech forests on Obzovica mt. |
III |
300 |
|
Catchment Area of Moraca River |
III |
86.000 |
|
In total, planned PAs 257.500 (č261.300) |
18,9% |
Protected Areas (PA), at present in Serbia
Category A
Zaštićena prirodna baština /Protected areas |
Number |
Area ( ha) |
1. Nacionalni parkovi National parks 2. Parkovi prirode Nature parks 3. predeli izuzetnih odlika Areas of Exeptional Natural Values |
5 15 15 |
159986 238135 32026 |
4. Strogi rezervati prirode Strict Nature Reserves 5.Specijalni rezervati prirode Special Nature Reserves |
50 20 |
2402 81427 |
6.SPOMENICI PRIRODE Nature monuments
6.a. Dendro-botanički/ dendro-botanical: (znamenita stabla i grupe stabala/tree-monument and tree groups, drvoredi/alley, park šume/park-wood, botanički lokaliteti/botanical locality, parkovi/parks, male šumske sastojine/ small wood content) |
282 221 |
7779 |
6.b.Objekti geo-nasledja/ Natural monument of geological features: (klisure i kanjon/ gorge and canyon, pećine i kraške jame/caves and carst pit, izvori i vrela/spring, prerasti i prozorci/overgrow, vidikovci/viewing spot,drugi oblici reljefa/other shape of relievo, značajna geološka mesta/important geological areas) |
60 |
|
7. KULTURNO-ISTORIJSKI PREDELI Areas of cultural and historical significance (memorijalni prirodni spomenici prostori oko nepokretnih kulturnih dobara/ Memorial natural monument and Natural area around cultural heritage site or monument |
37 |
3565 |
Total |
424 |
524320 |
Category B:
ZAŠTIĆENE VRSTE DIVLJE FLORE I FAUNE/PROTECTED WILD FLORA AND FAUNA SPECIES –Regulation of the Governament about protection of natural rarities (1993) and Regulation of the Governament puting under control of using and trade wild flora and fauna (2005)
1.PRIRODNE RETKOSTI/ NATURAL RARITIES PLANT SPECIES: 215 taxa species and sub- species wild flora, 427 taxa wild fauna.
2. KONTROLISANE VRSTE/CONTROL SPCIES: 3 specis of lichen , 15 fungi species, 152 planta species and 9 fauna species.
List of endangered natural habitats requiring specific conservation measures in Serbia and Montenegro (Resolution No. 4 (1996))
According to Resolution No. 6 (1998) of the Standing Committee national team have identified 315 endangered natural habitat in Serbia and Montenegro.
See Annex 1. of this report.
List of species requiring specific habitat conservation measures in Serbia and Montenegro (Resolution No. 6 (1998) of the Standing Committee)
According to Resolution No 4 (1996) national team have identified 199 fauna species and 24 flora species in Serbia and Montenegro.
See Annex 2. of this report.
List of biogeographical zones in country
Following biogeographical regions are present in Serbia and Montenegro:
- Panonnian
- Continental
- Alpine
- Mediterranean.
Selection of potential Areas of Special Conservation Interest (ASCI)
After identification of Emerald species listed in Resolution No.6 (1998) and Emerald habitat listed in Resolution No. 4 (1996) present in Serbia and Montenegro, potential Areas of Special Conservation Interest (ASCI) were selected based on the criteria listed in the Recommendation No. 16 (1989).
The selected sites are:
Sites have been chosen with total area of 336.113 ha.
For each of the mentioned sites a special Standard data form was filed to the Emerald software version 2.0.
See Annex 3. Map of selected site in Serbia and Montenegro.
-Problems and solutions
During the realization of Emerald pilot project national team identified some problems:
- Lack of data base for vegatation, especally for certain areas. Existing data is not in accordance with modern habitats classification system
- Information are fragmented and outdated
- Different stage of the research among certain areas
- Large number of endemic species which exist in Serbia and Montenegro have not been include in Emerald list
- Lack of experience in applying habitats classification system
- Lack of experience in Assessment for the Habitat (Representatively, Relative Surface, Conservation Status, Conservation of functions, Restoration possibilities) and Species (Size and density of the population, Degree of conservation, Restoration possibilities, etc.)
- Legislative basis for establishment of the Emerald still is not finally set;
- Technical problems with software
National team have been participated in a varius workshops in a field of nature protection and protected areas. In a framework of REReP project '' Promotion of networks and exchange in counties of South-Eastern Europe'' montenegrian experts exchange experiance with bulgarian and albanian experts about system of protected areas, Emerald network, costrains and problems in this project.
National team also introduce and promote Emerald network in Serbia and Montenegro on different TV stations and through educational programme.
Follow up activities
The country intends to carry out the secound implementation phaze (during 2006) by identifying 80% of the potential ACSIs.
In second phaze the work of team of expert will be focused in more areas where little work is done so far e.g. in the field of marine habitats and habitats proposed to be include in a category of protected areas. Special assesment activities are required to obtain information of these species and sites.
Future work for developing Emerald network in Serbia and Montenegro will greatly benefit from information and research through the UNDP projects such us Biodiversity Strategy, and other ongoing programmes targeted protected areas.
Proposal for expansion of Emerald species list
National team analyze which species should be added to the Emerald lists considering some specifications of Serbia and Montenegro.
Regarding the expansion of species list, the expert group decided to add the following species:
- local endemic species
- sub-endemic species
- marine species from the list of the Barcelona convention
See Annex 4. of this report.
Annexe 1 |
|||||
List of endangered natural habitats requiring specific conservation measures in Serbia and Montenegro |
|||||
Code |
HABITAT |
Total Serbia&Mon |
Serbia |
Montenegro |
Common S&M |
315 |
150 |
95 |
71 |
||
1. |
COASTAL AND HALOPHYTIC COMMUNITIE |
||||
11. |
OCEAN AND SEAS, MARINE COMMUNITIES |
||||
!11.2 |
Benthic communities |
+ |
+ |
||
!11.22 |
Sublittoral soft seabeds |
+ |
+ |
||
!11.24 |
Sublittoral rocky seabeds and kelp forests |
+ |
+ |
||
!11.25 |
Sublittoral organogenic concretions |
+ |
+ |
||
!11.26 |
Sublittoral cave communities |
+ |
+ |
||
!11.27 |
Soft sediment littoral communities |
+ |
+ |
||
!11.3 |
Sea-grass meadows |
+ |
+ |
||
!11.4 |
Brackish sea vascular vegetation |
+ |
+ |
||
!11.42 |
Marine spike-rush beds |
+ |
+ |
||
13 |
ESTUARIES AND TIDAL RIVERS |
+ |
|||
!13.2 |
Estuaries |
+ |
? |
||
!14. |
MUD FLATS AND SAND FLATS |
+ |
+ |
||
15. |
SALTMARSHES, SALT STEPPES, SALT SCRUBS, SALT FORESTS |
||||
!15.115 |
Continental glasswort swards <Salicornia europaea> |
+ |
+ |
||
!15.11511 |
Pannonian <Salicornia europaea> swards |
+ |
+ |
||
!15.11512 |
Pannonian seablite swards |
+ |
+ |
||
!15.11513 |
Pannonian saltswort communities |
+ |
+ |
||
!15.141 |
Ponto-Pannonian<Acorellus>communities |
+ |
+ |
||
!15.142 |
Central-eurasian<Crypsis>communities |
+ |
+ |
||
!15.143 |
Central-eurasian<Chenopodium> |
+ |
+ |
||
!15.4 |
Suboceanic inland salt meadows |
+ |
+ |
||
!15.41 |
Interior European saltmarsh grass meadows |
+ |
+ |
||
!15.42 |
Interior European saltmarsh rush and couch beds |
+ |
+ |
||
!15.5 |
Mediterranean salt meadows |
+ |
+ |
||
16 |
COASTAL SAND DUNES AND SAND BEACHES |
+ |
+ |
||
!16.2 |
Dunes |
+ |
+ |
||
2. |
NON-MARINE WATERS |
||||
22 |
STANDING FRESH WATER |
||||
!22.1 |
Permanent ponds and lakes |
+ |
+ |
||
!22.11 |
Lime-deficient oligotrophic waterbodies |
+ |
+ |
+ |
|
!22.146 |
Aldrovanda communities |
+ |
+ |
||
!22.3 |
Amphibious communities |
+ |
+ |
||
!22.31 |
Euro-Siberian perennial amphibious communities |
+ |
+ |
||
!22.312 |
<Eleocharis> swards |
+ |
+ |
||
!22.321 |
Dwarf spike-rush communities<Eleocharis> |
+ |
+ |
||
!22.323 |
Dwarf toad-rush communities |
+ |
+ |
||
!22.3232 |
Small galingale swards <Cyperus> |
+ |
+ |
||
!22.3233 |
Wey ground dwarf herb communities |
+ |
+ |
||
!22.34 |
Mediterraneo-Atlantic amphibious communities |
+ |
+ |
||
!22.341 |
Short Mediterranean amphibious swards |
+ |
+ |
||
!22.3414 |
Mediterranean small galingale swards |
+ |
+ |
||
!22.3415 |
Mediterranean [Fimbristylis] swards |
+ |
+ |
||
!22.3419 |
Mediterranean dwarf [Scirpus] swards |
+ |
+ |
||
!22.341A |
Mediterranean [Eleocharis] swards |
+ |
+ |
||
!22.342 |
Tall Mediterranean amphibious swards |
+ |
+ |
||
!22.344 |
Serapias grasslands |
+ |
+ |
||
!22.351 |
Pannonic riverbank dwarf sedge communities <Carex> |
+ |
+ |
||
22,4 |
Euhydrophyte communities |
+ |
+ |
||
22,41 |
Free-floating vegetation |
+ |
+ |
||
!22.412 |
Frogbit rafts<Hydrocharis morsus-ranae> |
+ |
+ |
||
!22.413 |
Water-soldier raftd<Stratiotes aloides> |
+ |
+ |
||
!22.414 |
Bladderwort colonies<Utricularia> spp. |
+ |
+ |
||
!22.415 |
Salvinia covers |
+ |
+ |
||
!22.416 |
Aldrovanda communities |
+ |
+ |
||
22,43 |
Rooted floating vegetation |
+ |
+ |
||
22,432 |
Shallow-water floating communities |
+ |
+ |
||
!22.4321 |
Water crowfoot communities<Ranunculus sect. Bratrachium> |
+ |
+ |
||
!22.4323 |
Water violet bads<Hottonia palustris> |
+ |
+ |
||
!22.44 |
Chandalier algae submerged carpets |
+ |
+ |
||
!22.5 |
Turlough and lake-bottom meadows |
+ |
+ |
||
23. |
STANDING BRACKISH AND SALT WATER |
||||
!23.11 |
Athalassall saline lakes |
+ |
+ |
||
!23.12 |
Submerged charophyte carpets in inland saline or hypersaline |
+ |
+ |
||
!23.13 |
Salt basin benthic communities |
+ |
+ |
||
!23.14 |
Exposed unvegetated beaches of inland saline and brackish waters with soft sediments |
+ |
+ |
||
24. |
RUNNING WATER |
||||
!24.2 |
River gravel banks |
+ |
+ |
||
!24.21 |
Unvegetated river gravel banks |
+ |
+ |
||
!24.22 |
Sparsely vegetated river gravel banks |
+ |
+ |
||
!24.221 |
Boreo-alpine stream gravel communities |
+ |
+ |
||
!24.222 |
Montane river gravel communities |
+ |
+ |
||
3. |
SCRUB AND GRASSLAND |
||||
31. |
TEMPERATE HEATH AND SCRUB |
+ |
+ |
||
!31.2 |
European dry heaths |
+ |
+ |
||
!31.22 |
Sub-Atlantic [Calluna] - [Genista] heaths |
+ |
+ |
||
31,4 |
Alpine and boreal heaths |
+ |
+ |
||
!31.46 |
Bruckenthalia heaths |
+ |
+ |
||
!31.461 |
Rhodopide [Bruckenthalia] heaths |
+ |
+ |
||
!31.462 |
North-western Hellenide [Bruckenthalia] heaths |
+ |
+ |
||
!31.463 |
Carpatho-Balkanic [Bruckenthalia] heaths |
+ |
+ |
||
!31.4631 |
Balkan range [Bruckenthalia] heaths |
+ |
+ |
||
!31.7 |
Hedgehog‑heaths |
+ |
+ |
||
!31.78 |
Helleno-Balkanic sylvatic [Astragalus] hedgehog-heaths |
+ |
+ |
||
!31.782 |
Moesian [Astragalus angusiifolius] hedgehog-heaths |
+ |
+ |
||
!31.8B1 |
Pannonic and sub‑Pannonic thickets |
+ |
+ |
||
!31.8B121 |
Peri-Pannonic ground cherry scrub |
+ |
+ |
||
!31.8B122 |
Peri-Pannonic dwarf almond scrub |
+ |
+ |
||
!31.8B125 |
Danubian hawthorn scrub |
+ |
+ |
||
!31.8B131 |
Peri-Pannonic hawthorn-blackthorn scrub |
+ |
+ |
||
!31.8B133 |
Pannonic wig tree-manna ash thickets |
+ |
+ |
||
32 |
SCLEROPHYLLOUS SCRUB |
||||
32,2 |
Thermo-Mediterranean shrub formations |
+ |
+ |
||
!32.22 |
Tree-spurge formations |
+ |
+ |
||
33. |
Phrygana |
+ |
+ |
||
34. |
STEPPES AND DRY CALCAREOUS GRASSLANDS |
||||
!34.112 |
Houseseleek communities<Semperivivum> <Jovibarba> |
+ |
+ |
||
!34.3 |
Dense perennial grasslands and middle European steppes |
+ |
+ |
||
!34.311 |
Helleno-Balkanic [Satureja montana] steppes |
+ |
+ |
||
!34.3161 |
Moesian-Carpathian steppes |
+ |
+ |
||
!34.31612 |
Moesian-Carpathian andropogonid steppes |
+ |
+ |
||
!34.3163 |
Moesian-Carpathian meadow steppes |
+ |
+ |
||
!34.31632 |
Moesian<Chrysopogon>meadow-steppes |
+ |
+ |
||
!34.31633 |
Moesian<Danthonia><Sieglinga>meadow-steppes |
+ |
+ |
||
34.32 |
Sub-Atlanticsemi-dry calcareous grassland |
+ |
+ |
||
34,329 |
Illyrian (Mesobromion) grasslands |
+ |
+ |
||
!34.3292 |
Illyrian<Seslaria>grasslands |
+ |
+ |
||
!34.37 |
Serpentine steppes |
+ |
+ |
||
!34.5 |
Mediterranean xeric grasslands |
+ |
+ |
||
!34.53 |
East Mediterranean xeric grassland |
+ |
+ |
||
!34.532 |
Helleno-Balkanic communities and terophyt |
+ |
+ |
||
!34.9 |
Continental steppes |
+ |
+ |
||
!34.911 |
Pannonic loess steppes |
+ |
+ |
||
!34.912 |
Pannonic tall forb meadow-steppes |
+ |
+ |
||
!34.913 |
Pannonic tall forb meadow-steppes |
+ |
+ |
||
!34.914 |
Pannonic loess pastures |
+ |
+ |
||
!34.A |
Sand steppes |
+ |
+ |
||
!34.AIII |
Drooping brome pioneer swards |
+ |
+ |
||
!34.A112 |
Corispermum pioneer swards |
+ |
+ |
||
!34.A1213 |
Southern Pannonic calciphile sand fescue steppes |
+ |
+ |
||
!34.A12122 |
Southern Pannonic feathergrass sand steppes |
+ |
+ |
||
!34.A132 |
Deliblat <Festuca wagneri> sand steppes |
+ |
+ |
||
!34.A14 |
Pannonic closed sand steppes |
+ |
+ |
||
!34.A15 |
Pannonic sand puszta |
+ |
+ |
||
!34.A12122 |
Southern Pannonic feathergrass sand steppes |
+ |
+ |
||
35 |
DRY SILICEOUS GRASSLANDS |
||||
!35.1 |
Atlantic mat-grass swards and related communities |
+ |
+ |
||
!35.11 |
Mat-grass swards <Nardus stricta> |
+ |
+ |
||
!35.115 |
Illyrian mat-grass swards |
+ |
+ |
||
!35.7 |
Mediterraneo-montane mat-grass swards |
+ |
+ |
||
!35.73 |
Balkanic montane mat-grass swards |
+ |
+ |
||
37 |
HUMID GRASSLAND AND TALL HERB COMMUNITIES |
||||
!37.2 |
Eutrophic humid grasslands |
+ |
+ |
||
!37.21 |
Atlantic and sub-Atlantic humid meadows |
+ |
+ |
||
!37.213 |
<Deschampsia caespitosa>meadows |
+ |
+ |
||
!37.215 |
<Polygonium bistorta> meadows |
+ |
+ |
||
!37.217 |
<Juncus effusus>meadows |
+ |
+ |
||
!37.219 |
<Scirpus sylvaticus>meadows |
+ |
+ |
||
!37.23 |
Subcontinental riverine meadows |
+ |
+ |
||
!37.24 |
Flood swards and related communities |
+ |
+ |
||
!37.241 |
Tall rush pastures |
+ |
+ |
||
!37.2424 |
<Agropyrum repens> swards |
+ |
+ |
||
!37.25 |
Transitional tall herb humid meadows |
+ |
+ |
||
!37.263 |
Dunabian-Pannonian riverian and humid meadows |
+ |
+ |
||
!37.3 |
Oligotrophic humid grasslands |
+ |
+ |
||
!37.31 |
[Molinia caerulea] meadows and related communities |
+ |
+ |
||
!37.313 |
Giant moorgrass swards |
+ |
+ |
||
!37.33 |
Continental oligotrophic humid grasslands |
+ |
+ |
||
!37.711 |
Angelica archangelica fluvial communities |
+ |
+ |
||
!37.713 |
Marsh mallow screens<Althaea officinalis> |
+ |
+ |
||
!38.25 |
Continental meadows |
+ |
+ |
||
!38.251 |
Ponto-Pannonian mezofilian high meadows |
+ |
+ |
||
4. |
FORESTS |
||||
41. |
BROAD-LEAVED DECIDUOUS FORESTS |
||||
!41.1 |
Beech forests |
+ |
+ |
||
!41.19 |
Moesian beech forests |
+ |
+ |
||
!41.1C |
Illyrian beech forests |
+ |
+ |
||
!41.1C222 |
Illyrian low-montane neutrophile fir-beech forests |
+ |
+ |
||
!41.1C3 |
Illyrian thermophile beech forests |
+ |
+ |
||
!41.1C31 |
Illyrian coastal beech forests |
+ |
+ |
||
!41.1C32 |
Illyrian inland calciphile beech forests |
+ |
+ |
||
!41.1C323 |
Illyrian (Acer obtusatum) beech forests |
+ |
+ |
||
!41.1C4 |
Illyrian subalpine beech forests |
+ |
+ |
||
!41.19312 |
<Prunus laurocerasus><Fagus>beech forests Old mountains(Blacanian mn.) |
+ |
+ |
||
!41.2 |
Oak-hornbeam forests |
+ |
+ |
||
!41.2A |
Illyrian oak - hornbeam forests |
+ |
+ |
||
!41.2A1 |
Illyrian sessile oak-hornbeam forests |
+ |
+ |
||
!41.2A12 |
Illyrian neutrocline sessile oak-hornbeam forests |
+ |
+ |
||
!41.2A2 |
Illyrian pedunculate oak-hornbeam forests |
+ |
+ |
||
!41.2B1 |
Pannonic hygrophile ash-oak-hornbeam forests |
+ |
+ |
||
!41.2B2 |
Peri-Pannonic acidophile oak-hornbeam forests |
+ |
+ |
||
!41.2C |
Southeastern European oak - hornbeam forests |
+ |
+ |
||
!41.2C3 |
Moesian oak-hornbeam forests |
+ |
+ |
||
!41.2C31 |
Moesian mesophile oak-hornbeam forests |
+ |
+ |
||
!41.2C32 |
Moesian thermophile oak-hornbeam forests |
+ |
+ |
||
!41.4 |
Mixed ravine and slope forests |
+ |
+ |
||
!41.462 |
Moesian ravine and slope forests |
+ |
+ |
||
!41.463 |
Illyrian ravine forests |
+ |
+ |
||
!41.4632 |
Illyrian mixed sycamore ravine forests |
+ |
+ |
||
!41.5 |
Acidophilous oak forests |
+ |
+ |
||
!41.57 |
Medio-European acidophilous [Quercus] forests |
+ |
+ |
||
!41.7 |
Thermophilous and supra-Mediterranean oak woods |
+ |
+ |
||
!41.73 |
Eastern [Quercus pubescens] woods |
+ |
+ |
||
!41.74 |
Italo-Illyrian [Ostrya carpinifolia] sub-thermophilous [Quercus] |
+ |
+ |
||
!41.736 |
Dalmatian white oak woods |
+ |
+ |
||
!41.737 |
Eastern sub-Mediterranean white oak woods |
+ |
+ |
||
!41.7372 |
Moesian white oak woods |
+ |
+ |
||
!41.7374 |
Pannonian [Quercus pubescens] woods |
+ |
+ |
||
!41.7375 |
Illyrian [Quercus pubescens] |
+ |
+ |
||
!41.74 |
Italo-Illyrian [Ostrya carpinifolia] sub-thermophilous [Quercus] woods |
+ |
+ |
||
!41.742 |
Dalmatian thermophile turkey oak-sessile oak woods |
+ |
+ |
||
!41.7421 |
Dalmatian [Quercus cerris] woods |
+ |
+ |
||
!41.7422 |
Dalmatian [Quercus petraea] woods |
+ |
+ |
||
!41.761 |
Helleno-Moesian<Quercus cerris> woods |
+ |
+ |
||
!41.762 |
Helleno-Moesian<Quercus frainetto> woods |
+ |
+ |
||
!41.763 |
Helleno-Moesian<Quercus daleachampii>woods |
+ |
+ |
||
!41.7641 |
Helleno-Moesian<Quercus petrea>woods |
+ |
+ |
||
!41.765 |
Helleno-Moesian<Quercus virgiliana>woods |
+ |
+ |
||
!41.766 |
Helleno-Moesian<Quercus pedunculiflora>woods |
+ |
+ |
||
!41.767 |
Helleno-Moesian <Quercus polycarpa> forests |
+ |
+ |
||
!41.78 |
[Quercus trojana] woodland |
+ |
+ |
||
!41.781 |
Helleno-Balkanic Trojan oak woods |
+ |
+ |
||
!41.7A12 |
Pannonic turkey oak-sessile oak woods |
+ |
+ |
||
!41.7A13 |
Pannonic hairy greenweed sessile oak woods |
+ |
+ |
||
!41.7A2133 |
Voivodinian sand steppe oak woods |
+ |
+ |
||
!41.8 |
Mixed thermophilous forests |
+ |
+ |
||
!41.81 |
Hop-hornbeam woods |
+ |
+ |
||
!41.812 |
Supra-Mediterranean hop-hornbeam woods |
+ |
+ |
||
!41.8123 |
Eastern Adriatic supra-Mediterranean hop-hornbeam woods |
+ |
+ |
||
!41.82 |
Oriental hornbeam woods |
+ |
+ |
||
!41.822 |
Helleno-Balkanic oriental hornbeam woods |
+ |
+ |
||
!41.8222 |
Moesian oriental hornbeam woods |
+ |
+ |
||
!41.8223 |
Lilac oriental hornbeam woods |
+ |
+ |
||
!41.8225 |
Eastern Adriatic oriental hornbeam woods |
+ |
+ |
||
!41.834 |
Moesian thermophilous maple woods |
+ |
+ |
||
!41.84 |
Thermophilous [Tilia] woods |
+ |
+ |
||
!41.85 |
[Celtis australis] woods |
+ |
+ |
||
!41.863 |
Manna tree woods |
+ |
+ |
||
!41.87 |
Pannonic [Juniperus] - [Populus] steppe woods |
+ |
+ |
||
!41.88 |
Sub-Mediterranean and Pannonic mixed woods |
+ |
+ |
||
!41.891 |
Western Asian wild fruit tree steppe woods |
+ |
+ |
||
42. |
TEMPERATE CONIFEROUS FORESTS |
||||
!42.16 |
South Balcan silver fir forest |
+ |
+ |
||
!42.17 |
Balkano-Pontic fir forest |
+ |
+ |
||
42,2 |
Western Palaearctic orogenous spruce forests |
+ |
+ |
||
42,24 |
Sub-Mediterranean Norway spruce forests |
+ |
+ |
||
!42.243 |
Montenegrine spruce forest |
+ |
+ |
||
!42.244 |
Paeonician spruce forest |
+ |
+ |
||
!42.245 |
Balkan Range spruce forest |
+ |
+ |
||
!42.27 |
Omorike spruce forest<Picea omorika> |
+ |
+ |
||
42.5 |
Western Palaearctic Scots pine forests |
+ |
+ |
||
!42.5C |
South-eastern European Scots pine forests |
+ |
+ |
||
!42.5C6 |
Dinaric calcicole Scots pine forests |
+ |
+ |
||
!42.6 |
Black pine forests |
+ |
+ |
||
!42.62 |
Western Balkan Pinus nigra forests |
+ |
+ |
||
!42.621 |
Dinaro-Pelagonian Pinus nigra forests |
+ |
+ |
||
!42.6215 |
Illyrian submediterranean Pinus nigra forests |
+ |
+ |
||
!42.66 |
Banat and Pallas pine forest |
+ |
+ |
||
!42.7 |
High oro-mediterranean pine forests |
+ |
+ |
||
!42.71 |
White-barked pine [Pinus leucodermis] forests |
+ |
+ |
||
!42.715 |
South Dinaric white-barked pine forests |
+ |
+ |
||
!42.72 |
Macedonian pine [Pinus peuce] woods |
+ |
+ |
||
!42.722 |
Southern Dinaric Macedonian pine woods |
+ |
+ |
||
44 |
TEMPERATE RIVERINE AND SWAMP FORESTS AND BRUSH |
||||
!44.1 |
Riparian willow formations |
+ |
+ |
||
!44.11 |
Orogenous riverine brush |
+ |
+ |
||
!44.12 |
Lowland and collinar riverine [Salix] scrub |
+ |
+ |
||
!44.13 |
Middle European [Salix alba] forests |
+ |
+ |
||
!44.121 |
Almond willow-osier scrub |
+ |
+ |
||
!44.123 |
Balkan riverine willow scrub |
+ |
+ |
||
!44.14 |
Mediterranean tall [Salix] galleries |
+ |
+ |
||
!44.161 |
Pannonic willow galleries |
+ |
+ |
||
!44.141 |
Mediterranean white willow galleries |
+ |
+ |
||
!44.1412 |
Eumediterranean white and crack willow galleries |
+ |
+ |
||
!44.2 |
Boreo-alpine riparian galleries |
+ |
+ |
||
!44.21 |
Montane grey alder galleries |
+ |
+ |
||
!44.215 |
Montenegrine grey alder galleries |
+ |
+ |
||
!44.24 |
Boreal black alder galleries |
+ |
+ |
||
!44.3 |
Middle European stream ash‑alder woods |
+ |
+ |
||
!44.31 |
[Fraxinus] - [Alnus] woods of rivulets and springs |
+ |
+ |
||
!44.32 |
[Fraxinus] - [Alnus] woods of fast-flowing rivers |
+ |
+ |
||
!44.33 |
[Fraxinus] - [Alnus] woods of slow rivers |
+ |
+ |
||
44,4 |
Mixed oak-elm-ash forests of great rivers |
+ |
+ |
||
!44.43 |
South-east European ash-oak-alder forests |
+ |
+ |
||
!44.432 |
Helleno-Balkanic ash-oak-alder forests |
+ |
+ |
||
!44.4325 |
Montenegrine ash-oak-alder forests |
+ |
+ |
||
!44.5 |
Southern alder and birch galleries |
+ |
+ |
||
!44.51 |
Southern black alder galleries |
+ |
+ |
||
!44.8 |
Southern riparian galleries and thickets |
+ |
+ |
||
!44.81 |
[Nerium oleander] [Vitex agnus-castus] and [Tamarix] galleries |
+ |
+ |
||
!44.812 |
Chaste tree thickets |
+ |
+ |
||
!44.813 |
Mediterraneo-Macaronesian tamarisk thickets |
+ |
+ |
||
44,9 |
Alder, willow, oak, aspen swamp woods |
+ |
+ |
||
44,914 |
Steppe swamp alder woods |
+ |
+ |
||
!44.9141 |
Pannonic swamp alder-ash woods |
+ |
+ |
||
! 45. |
TEMPERATE BROAD‑LEAVED EVERGREEN FORESTS |
+ |
+ |
||
45.11 |
Wild olive woodland |
+ |
? |
||
45.12 |
Carob woodland |
+ |
? |
||
45,3 |
Holm-oak forests |
+ |
+ |
||
45.319 |
Illyrian holm-oak woodland |
+ |
+ |
||
45,4 |
Kermes oak forests |
+ |
+ |
||
45,5 |
Eurasian continental lauriphyllous forests |
+ |
+ |
||
45,51 |
Mediterraneo-Atlantic laurel-oak woodland |
+ |
+ |
||
5. |
BOGS AND MARSHES |
||||
51. |
RAISED BOGS |
||||
!51.1 |
Near‑natural raised bogs |
+ |
+ |
||
!51.13 |
Bog pools |
+ |
+ |
||
!51.131 |
Bog eye (kolk) |
+ |
+ |
||
53. |
WATER-FRINGE VEGETATION |
||||
!53.3 |
Fen-sedge beds |
+ |
+ |
||
!53.31 |
Fen [Cladium mariscus] beds |
+ |
+ |
||
!53.33 |
Riparian [Cladium] beds |
+ |
+ |
||
54. |
FENS, TRANSITION MIRES AND SPRINGS |
||||
54,1 |
Springs |
+ |
+ |
||
!54.12 |
Hard water springs |
+ |
+ |
||
!54.2 |
Rich fens |
+ |
+ |
||
!54.21 |
Tall herb fens |
+ |
+ |
||
!54.22 |
[Schoenus ferrugineus] fens |
+ |
+ |
||
!54.25 |
[Carex dioica], [Carex pulicaris] and [Carex flava] fens |
+ |
+ |
||
!54.26 |
[Carex nigra] alkaline fens |
+ |
+ |
||
!54.214 |
Illyrian black bogrush fens |
+ |
+ |
||
!54.23 |
Subcontinental Davall sedge fens |
+ |
+ |
||
!54.236 |
Dinaric carnation-tawny sedge fens |
+ |
+ |
||
!54.2F |
Middle European flat sedge fens |
+ |
+ |
||
!54.3 |
Arcto-alpine riverian swards |
+ |
+ |
||
54,4 |
Acidic fens |
+ |
+ |
||
54,42 |
Black-white-star sedge fens |
+ |
+ |
||
!54.426 |
Peri-Danubian black-white-star sedge fens |
+ |
+ |
||
!54.4262 |
Dinaric black-star sedge acidic fens |
+ |
+ |
||
!54.4263 |
Rhodopide black-star sedge acidic fens |
+ |
+ |
||
!54.4265 |
Balkanic black-star sedge fens |
+ |
+ |
||
!54.4266 |
Moeso-Macedonian black-star sedge fens |
+ |
+ |
||
!54.5 |
Transition mires |
+ |
+ |
||
!54.51 |
Slender-sedge swards |
+ |
+ |
||
!54.513 |
Brown moss-sphagnum slender-sedge swards |
+ |
+ |
||
!54.52 |
[Carex diandra] quaking mires |
+ |
+ |
||
!54.53 |
Bottle sedge quaking mires |
+ |
+ |
||
!54.532 |
Basicline bottle sedge quaking mires |
+ |
+ |
||
!54.5321 |
Basicline sphagnum-bottle sedge quaking mires |
+ |
+ |
||
!54.54 |
[Carex limosa] swards |
+ |
+ |
||
!54.57 |
[Rhynchospora alba] quaking bogs |
+ |
+ |
||
!54.58 |
Sphagnum and cottongrass rafts |
+ |
+ |
||
!64 |
INLAND SAND DUNES |
||||
!64.711 |
Pannonic bare sands |
+ |
+ |
||
!64.712 |
Pannonic dune lichen communities |
+ |
+ |
||
!64.713 |
Pannonic dune pioneer grasslands |
+ |
+ |
||
!64.714 |
Pannonic dune open grasslands |
+ |
+ |
||
!64.715 |
Pannonic dune closed grasslands |
+ |
+ |
||
!64.716 |
Pannonic dune thickets and scrubs |
+ |
+ |
||
!64.717 |
Pannonic dune woods |
+ |
+ |
||
6. |
INLAND ROCKS, SCREES AND SANDS |
||||
!65. |
Caves |
+ |
+ |
||
!65.4 |
Troglobiont invertebrate caves |
+ |
+ |
||
!65.5 |
Troglophile invertebrate caves |
+ |
+ |
||
!65.6 |
Subtroglophile invertebrate caves |
+ |
+ |
||
!93 |
WOODED STEPPE |
+ |
+ |
||
Annex 2 |
||||
List of endangered species requiring specific conservation measures in Serbia and Montenegro |
||||
Total Serbia&Mon |
Serbia |
Montenegro |
Common S&M |
|
SPECIES |
199 |
159 |
154 |
111 |
VERTEBRATES/VERTÉBRÉS |
||||
Mammals/Mammifères |
||||
CHIROPTERA |
||||
Rhinolophidae |
+ |
+ |
+ |
|
Rhinolophus blasii |
+ |
+ |
+ |
+ |
Rhinolophus euryale |
+ |
+ |
+ |
+ |
Rhinolophus ferrumequinum |
+ |
+ |
+ |
+ |
Rhinolophus hipposideros |
+ |
+ |
+ |
+ |
Rhinolophus mehelyi |
+ |
|||
Vespertilionidae |
+ |
+ |
||
Barbastella barbastellus |
+ |
+ |
+ |
|
Miniopterus schreibersi |
+ |
+ |
+ |
+ |
Myotis bechsteini |
+ |
+ |
+ |
+ |
Myotis blythii |
+ |
+ |
+ |
+ |
Myotis capaccinii |
+ |
+ |
+ |
+ |
Myotis dasycneme |
+ |
+ |
+ |
+ |
Myotis emarginatus |
+ |
+ |
+ |
+ |
Myotis myotis |
+ |
|||
RODENTIA |
||||
Sciuridae |
+ |
+ |
+ |
|
Spermophilus citellus (Citellus citellus)# |
+ |
|||
Castoridae |
+ |
+ |
||
Castor fiber # 1, 2 |
||||
CARNIVORA |
||||
Canidae |
+ |
+ |
+ |
|
Ursidae |
+ |
+ |
+ |
|
Ursus arctos # 1 |
+ |
|||
Mustelidae |
+ |
+ |
||
Lutra lutra # |
+ |
+ |
||
Mustela lutreola |
||||
Felidae |
+ |
+ |
+ |
|
Lynx lynx # 1 |
+ |
|||
Phocidae |
+ |
+ |
||
Monachus monachus |
||||
Birds/Oiseaux |
||||
GAVIIFORMES |
||||
Gaviidae |
+ |
+ |
||
Gavia stellata |
+ |
+ |
||
Gavia arctica |
+ |
+ |
||
Gavia immer |
||||
PODICIPEDIFORMES |
||||
Podicipedidae |
+ |
+ |
||
Podiceps auritus |
||||
PROCELLARIIFORMES |
||||
Hydrobatidae |
+ |
+ |
||
Hydrobates pelagicus |
||||
Procellariidae |
+ |
+ |
||
Calonectris diomedea |
+ |
+ |
||
Puffinus yelkouan yelkouan |
||||
PELECANIFORMES |
||||
Phalacrocoracidae |
+ |
+ |
+ |
|
Phalacrocorax pygmaeus |
+ |
|||
PELICANIFORMES |
+ |
+ |
||
Pelicanus crispus |
||||
CICONIIFORMES |