Group | NATURA 2000 - EUROPEAN UNION Animal SPECIES (Annex II, IV, V) in Serbia | Priority | Annex II | Annex IV | Amendments | Pannonian PAN | Continental CON | Overall knowledge (Annex II species) | Representativity (Annex II species) | Note General comment: Listed species of Annex II and Annex IV (+ Annex V for Fish species) Not included species which are occured only on territory of Kosovo & Metohija; X - presence - confirm on workshop 2019; experts assessment 2019 - 2021; working groups meetings 2021 | ||
---|---|---|---|---|---|---|---|---|---|---|---|---|
PAN | CON | PAN | CON | |||||||||
A | Bombina bombina | 1 | 1 | X | X | 2 | 2 | 2 | 4b | |||
A | Bombina variegata | 1 | 1 | X | X | 3 | 2 | 4b | 2 | |||
A | Hyla arborea | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
A | Pelobates fuscus | 0 | 1 | X | X | 2 | 3 | 2 | 4b | |||
A | Pelobates syriacus | 0 | 1 | X | X | 3 | 3 | 4b | 4b | |||
A | Pseudepidalea viridis (Bufo viridis) | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
A | Rana dalmatina | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
A | Rana esculenta (Pelophylax esculenta) | Annex V | ||||||||||
A | Rana graeca | 0 | 1 | X | 2 | 2 | ||||||
A | Rana lessonae (Pelophylax lessonae) | 0 | 1 | X | 2 | 3 | 2 | 4b | ||||
A | Rana ridibunda (Pelophylax ridibunda) | Annex V | ||||||||||
A | Rana temporaria | Annex V | ||||||||||
A | Salamandra atra | 0 | 1 | only in Kosovo; proposed for exclusion from ref.list | ||||||||
A | Triturus carnifex (T. macedonicus) | 1 | 1 | X | 2 | 3a | difference in scientific name (previous Triturus carnifex 1167) is due to a change in taxon concept (e.g. because previous species concept has been revised and split up in two species). | |||||
A | Triturus cristatus | 1 | 1 | X | X | 3 | 2 | 4a | 4a | |||
A | Triturus dobrogicus | 1 | 1 | 1 | X | X | 2 | 3 | 3a | 4a | The species is given as a proposal for amendments to the Annexes of Habitats Directive - proposal for Annex IV | |
A | Triturus karelinii (ivanbureschi) | 1 | 1 | X | 2 | 3a | ||||||
AI | Palingenia longicauda | 1 | 1 | 1 | X | 3 | 4a | |||||
B | Barbastella barbastellus | 1 | 1 | X | X | 3 | 2 | 4b | 4b | |||
B | Eptesicus serotinus | 0 | 1 | X | X | 2 | 2 | 3a | 3a | |||
B | Hypsugo savii (Pipistrellus savii) | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
B | Miniopterus schreibersii | 1 | 1 | X | X | 2 | 1 | 4a | 3a | |||
B | Myotis alcathoe | 0 | 1 | X | X | 2 | 2 | 4a | 3a | |||
B | Myotis bechsteinii | 1 | 1 | X | X | 2 | 2 | 4a | 4a | |||
B | Myotis blythii | 1 | 1 | X | X | 3 | 2 | 4a | 3a | |||
B | Myotis brandtii | 0 | 1 | ? SR | X | 5 | 3 | 6 | 4b | ? SR - PAN - Scientific reserve - needs further confirmation by field mapping | ||
B | Myotis capaccini | 1 | 1 | X | 1 | 1 | 0 | 3a | ||||
B | Myotis dasycneme | 1 | 1 | X | X | 2 | 3 | 3b | 4b | |||
B | Myotis daubentonii | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
B | Myotis emarginatus | 1 | 1 | X | X | 1 | 1 | 4a | 3a | |||
B | Myotis myotis | 1 | 1 | X | X | 3 | 1 | 4a | 3a | |||
B | Myotis mystacinus | 0 | 1 | X | X | 2 | 2 | 3a | 3a | |||
B | Myotis nattereri | 0 | 1 | X | X | 2 | 2 | 4a | 4a | |||
B | Nyctalus leisleri | 0 | 1 | X | X | 2 | 2 | 3a | 3a | |||
B | Nyctalus noctula | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
B | Pipistrellus kuhlii | 0 | 1 | X | X | 2 | 2 | 1 | 1 | |||
B | Pipistrellus nathusii | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
B | Pipistrellus pipistrellus | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
B | Pipistrellus pygmaeus | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
B | Plecotus auritus | 0 | 1 | X | X | 3 | 2 | 4a | 4a | |||
B | Plecotus austriacus | 0 | 1 | X | X | 2 | 2 | 4a | 4a | |||
B | Plecotus macrobullaris | 0 | 1 | X | 1 | 5 | 0 | 6 | ||||
B | Rhinolophus blasii | 1 | 1 | X | 1 | 1 | 0 | 4b | ||||
B | Rhinolophus euryale | 1 | 1 | X | X | 3 | 1 | 4a | 4a | |||
B | Rhinolophus ferrumequinum | 1 | 1 | X | X | 1 | 1 | 3a | 3a | |||
B | Rhinolophus hipposideros | 1 | 1 | X | 1 | 1 | 0 | 3a | ||||
B | Rhinolophus mehelyi | 1 | 1 | X | 1 | 3 | 0 | 4b | ||||
B | Tadarida teniotis | 0 | 1 | X | 1 | 3 | 0 | 4b | ||||
B | Vespertilio murinus | 0 | 1 | X | X | 2 | 2 | 4b | 4b | |||
Be | Bolbelasmus unicornis | 1 | 1 | X | X | 3 | 3 | 4b | 4b | more data for Bolbelasmus unicornis is available in Ćurčić et al. | ||
Be | Carabus hungaricus | 1 | 1 | X | ? | 3 | 3 | 4b | n/a | no data available; There are few recent finding of this species from pannonian region | ||
Be | Carabus variolosus | 1 | 1 | X | X | 3 | 2 | 4b | 3b | More data on Carabus variolosus is available for Vršac Mt., Fruška Gora, Zasavica, Juhor (Mesaroš, pers comm). The problem with species nomenclature exist. | ||
Be | Cerambyx cerdo | 1 | 1 | X | X | 1 | 2 | 4b | 4b | distribution map from BF 2019 as Cerambyx cerdo subsp. cerdo 2.doc | ||
Be | Cucujus cinnaberinus | 1 | 1 | X | 1 | 5 | 3b | n/a | Its presence in forests in the floodplain areas of Danube, Sava and Tisa is higly expected. It is not excluded that it is distributed further south (there are several specimens in the Museum of Natural History in Belgrade collected in 1934 around Kruševac) | |||
Be | Graphoderus bilineatus | 1 | 1 | X | ? | 3 | n/a | 4b | n/a | could be recorded in still water overgrown in Nymphaea sp; no data available from Continental r. There is an occurrence from around Majdanpek (Matić, 1922). In this moment there are no suitable habitats in that area | ||
Be | Limoniscus violaceus | 1 | 0 | X | n/a | 5 | n/a | 4b | New data for Limoniscus violaceus from Sopotnica (Gabor Mesaroš, unpublished data). Search for this species should be done during the night when more specimens are active. Sopotnica is in the Alpine region. There are also a published occurence from the Majdanpek forestry (šumska domena Živojinović, 1950). It's presence in that area can be expected. | |||
Be | Lucanus cervus | 1 | 0 | X | X | 1 | 1 | 3b | 3b | |||
Be | Morimus funereus | 1 | 0 | X | X | 1 | 1 | 3b | 3b | |||
Be | Osmoderma eremita | 1 | 1 | 1 | ? | X | 4 | 3 | n/a | 4b | ? - no data available from Pannonian region, the presence of this species in the Pannonian region is unlikely. They prefer veteran trees with big holes and cavities that were in Vojvodina cut out long time ago. All recent findings of this species is from the alpine region | |
Be | Phryganophilus ruficollis | 1 | 1 | 1 | 4 | 4 | n/a | n/a | old literature data, their exclusion/inclusion into the reference list will be disscuss | |||
Be | Pilemia tigrina | 1 | 1 | X | X | 3 | 3 | 4b | 4b | should be serched for in ruderal habitats, monophagous on Anchusa barrelieri. | ||
Be | Rhysodes sulcatus | 1 | 0 | 4 | 4 | n/a | n/a | old literature data, their exclusion/inclusion into the reference list will be disscuss | ||||
Be | Rosalia alpina | 1 | 1 | 1 | X | X | 3 | 1 | 4b | 3b | distribution map from BF 2019 as Rosalia alpina subsp. alpina 2.doc | |
Be | Stephanopachys substriatus | 1 | 1 | 4 | 4 | n/a | n/a | old literature data, their exclusion/inclusion into the reference list will be disscuss | ||||
Be | Tentyria frivaldszkii | 1 | 1 | 1 | X | X | 3 | 3 | 4a | n/a | This species is common on sandy habitats at right banks of the Danube river between Ram and Veliko Gradiste. | |
Bu | Apatura metis | 0 | 1 | X | x? | 3 | 5 | 4b | 4b | X? - Records from Kragujevac are a result of missidentification (Abadijev, 2006: https://www.biodiversitylibrary.org/part/194595). Recent records from Stara planina should be checked (Langourov, 2009: Ecologica Montenegrina, 20, 2019, 119-162). | ||
Bu | Arytrura musculus | 1 | 1 | X | X? | 3 | 5 | 4b | 6 | X? - CON - no recorded | ||
Bu | Callimorpha quadripunctaria/ 6199 Eupalagia quadripunctaria | 1 | 1 | 1 | X - SR | X - SR | 2 | 2 | 2 | 2 | European Commision mistake - this species should not be included to the Annexes, it is not sufficient to prepare special sites only for this species | |
Bu | Chondrosoma fiduciarium (fidiciaria) | 1 | 1 | ? | 5 | 6 | Species which was not recorded in Serbia, but their presence could be expected in Vojvodina, for its recent record in Ásotthalom. Hard to be recorded. Late October – early November. Host plants: Seseli tortuosum, Centaurea jacea, C. scabiosa, Achilea asplenifolia, Euphorbia sp... Wingless females. | |||||
Bu | Colias myrmidone | 1 | 1 | Ex (SR) | Ex (SR) | 4 | 4 | 6 | 6 | Excint - Scientific reserve - only old data are available (last 1993) | ||
Bu | Cucullia mixta | 1 | 1 | ? | 5 | 6 | Species which was not recorded in Serbia, but their presence could be expected. Host plant Aster (Galatella) linosyris, flies from late May to late June | |||||
Bu | Dioszeghyana schmidtii (schmidti) | 1 | 1 | X | X | 5 | 4 | 6 | 6 | |||
Bu | Erannis ankeraria | 1 | 1 | 5 | 3 | 6 | 4a | Species which was not recorded in Serbia, but their presence could be expected | ||||
Bu | Eriogaster catax | 1 | 1 | X | X | 2 / 3 | 5 | 3b | 3b | |||
Bu | Euphydryas aurinia | 1 | 1 | X? | X | 4 | 1 | 3b | 3b | X? - PAN - only old literature data available | ||
Bu | Euphydryas maturna (Hypodryas maturna) | 1 | 1 | X | X | 4 | 2 | 4b | 4b | |||
Bu | Glyphipterix loricatella | 1 | 1 | ? | ? | 5 | 6 | The species Glyphipterix loricatella is recorded by Meess & Spuler (1910) without precise locality. Its host plant is Iris sp. And is found in forest steppe, usually in calcareous area, more likely in Pannonian reg. | ||||
Bu | Gortyna borelii lunata | 1 | 1 | X | X | 2 | 5 | 4a | 6 | |||
Bu | Hyles hippophaes | 0 | 1 | Species which was not recorded in Serbia, but their presence could be expected | ||||||||
Bu | Leptidea morsei | 1 | 1 | Ex (SR) | ? | 4 | 4 | 6 | 6 | Extinct - no recent data | ||
Bu | Lignyoptera fumidaria | 1 | 1 | ? | ? | 5 | 6 | Species which was not recorded in Serbia, but their presence could be expected (Vojvodina?). Flying during the day.Xerothermous habitat, calcareous or dolometes. Probably polyphagous, usually on Achilea sp. | ||||
Bu | Lopinga achine | 0 | 1 | Ex (SR) | 5 | 6 | no recent data | |||||
Bu | Lycaena dispar | 1 | 1 | X | X | 2 | 2 | 2 | 2 | |||
Bu | Lycaena helle | 1 | 1 | X | 1 | 4b | ||||||
Bu | Maculinea (Phengaris) arion | 0 | 1 | X | X | 3 | 2 | 4b | 3b | |||
Bu | Maculinea (Phengaris) teleuis | 1 | 1 | X | 1 / 3 | 4b | ||||||
Bu | Nymphalis vaualbum | 1 | 1 | 1 | X? | X | 2 | 4b | X? - no pernament population | |||
Bu | Parnassius apollo | 0 | 1 | X | 2 | 4b | ||||||
Bu | Parnassius mnemosyne | 0 | 1 | X | X | 3 | 2 | 4b | 2 | |||
Bu | Phyllometra culminaria | 1 | 1 | ? | 5 | 6 | Species which was not recorded in Serbia, but their presence could be expected. It is found in western Hungary and considered as arelict of the steppe. Flying during the day. | |||||
Bu | Polyommatus eroides (eros) | 1 | 1 | X | 2 | 4a | ||||||
Bu | Proserpinus proserpina | 0 | 1 | X | X | 5 | 5 | 4b | 4b | |||
Bu | Pseudophilotes bavius | 1 | 1 | Kosovo i Metohija | ||||||||
Bu | Zerynthia (Zerynthia) polyxena | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
CF | Austropotamobius pallipes | 1 | 0 | 5 | 5 | 6 | 6 | Austropotamobius pallipes was found in Montenegro, in Zeta river and in Bosnia and Herzegovina on several localities (eastern borders of the species distribution). There is some possibility to record this species along Ibar and Lim rivers. | ||||
CF | Austropotamobius torrentium | 1 | 1 | 0 | X | X | 3 | 1 | 4b | 3b | ||
DF | Aeshna viridis | 0 | 1 | ? | 5 | 5 | 6 | 6 | old 1994 data record near Subotica; distribution map from BF 2019 as Aeshna viridis 2.doc; The species is strongly connected with water soldier (Stratiotes alloides) so I would personally (Miloš Jović) expect to find it in the near future in the lowlads of N Serbia (basically in Vojvodina). data from fulcrum database 2020 is not relevant (Pavol´s note) | |||
DF | Coenagrion ornatum | 1 | 0 | X | X | 5 | 5 | 4b | 4b | |||
DF | Cordulegaster heros | 1 | 1 | X | X | 2 | 2 | 4b | 3a | |||
DF | Leucorhinia pectoralis | 1 | 1 | X | X | 3 | 3 | 6 | 6 | Habitats where the species was previoulsy found in Serbia are either destroyed or going to be destroyed in quite a near future, due to production of an artificial lake (Vlasina) or climate change - drought (Selevenj). However, both locations are on the very borders with Bulgaria and Hungary (respectively). Having in mind that both bordering counties have populations of L. pectoralis, it seems we can expect immigration of the species as soon as we manage to maintain and protect suitable habitats. Moreover, some Serbian populations may be overlooked. | ||
DF | Leucorrhinia caudalis | 0 | 1 | ? | 5 | 5 | 6 | 0 | The last and only data from Serbia are from 1970-ies. It is most likely that the species is not present in Serbia anymore. However there are suitalbe habitats and there are good reasons to look for it in the province of Vojvodina) | |||
DF | Ophiogomphus cecilia | 1 | 1 | X | X | 5 | 5 | 4b | 4b | |||
DF | Stylurus (Gomphus) flavipes | 0 | 1 | X | X | 2 | 5 | 3b | 4b | The species is rather frequent along large lowland rivers (at least teh Danube and Sara rivers). It is recommneded to perform exuviae survey in late June - early July. | ||
F | Acipencer sturio | 1 | 1 | 1 | Ex | Ex | Ex - extinct in Danube | |||||
F | Acipenser nudiventris | 0 | 0 | Annex V | ||||||||
F | Acipenser ruthenus | 0 | 0 | Annex V | ||||||||
F | Acipenser stellatus | 0 | 0 | Annex V | ||||||||
F | Alosa spp. (A. imaculata sy. A. pontica 2491, A. tanaica) | 1 | 0 | X | probably SR Ref; Annex V | |||||||
F | Aspius aspius | 1 | 0 | X | X | 1 | 1 | 0 | 1 | |||
F | Barbus balcanicus | 0 | 0 | Annex V | ||||||||
F | Barbus barbus | 0 | 0 | Annex V | ||||||||
F | Barbus cyclolepis | 0 | 0 | Annex V | ||||||||
F | Barbus rebeli | 0 | 0 | Annex V | ||||||||
F | Chalcaburnus chalcoides (Alburnus chalcoides) | 1 | 0 | ? | X | |||||||
F | Cobitis elongata | 1 | 0 | X | X | 1 | 1 | 3b | 3b | |||
F | Cobitis taenia (Cobitis elongatoides) | 1 | 0 | X | X | 2 | 2 | 3b | 3b | |||
F | Cottus gobio | 1 | 0 | X | 2 | 2 | 3b | 3b | ||||
F | Eudontomyzon spp. (E.danfordi 4123, E.mariae 2484, E.stankokaramani) | 1 | 0 | X | X | 5 | 5 | 4b | 4b | |||
F | Eudontomyzon vladykovi | 1 | 0 | X | X | 5 | 5 | 5 | 6 | |||
F | Gobio albipinnatus | 1 | 0 | X | X | |||||||
F | Gobio kessleri | 1 | 0 | X | X | 2 | 2 | 4b | 4b | (Romanogobio kessleri 6143 + including Romanogobio banaticus 5327) | ||
F | Gobio uranoscopus | 1 | 0 | X | X | 5 | 5 | 4b | 4b | |||
F | Gymnocephalus baloni | 1 | 1 | X | ? | 2 | 2 | 4b | 4b | |||
F | Gymnocephalus schraetzer | 1 | 0 | X | X | 2 | 2 | 0 | 1 | Annex V | ||
F | Hucho hucho | 1 | 0 | X | 1 | 1 | 4b | 4b | Annex V | |||
F | Huso huso | 0 | 0 | Annex V | ||||||||
F | Leuciscus souffia (Telestes souffia) | 1 | 0 | X | 3 | 3 | 4b | 4b | ||||
F | Misgurnus fossilis | 1 | 0 | X | X | 2 | 2 | 4b | 4b | |||
F | Pelecus cultratus | 1 | 1 | X | X | 2 | 2 | 4b | 4b | Annex V | ||
F | Rhodeus sericeus amarus (Rhodeus amarus) | 1 | 0 | X | X | 1 | 1 | 0 | 1 | |||
F | Rutilus pigus (Rutilus pigus virgo 5345) | 1 | 0 | ? | ? | 1 | 1 | 4b | 4b | comment - WG meeting 20.4.2021 -Jasmina Krpo-Ćetković - "ne živi u Srbiji; pogrešno se vodi u pravilnicima umesto Rutilus virgo"; Annex V | ||
F | Sabanejewia aurata (S. balcanica 5197; S.bulgarica 5347) | 1 | 0 | X | 1 | 1 | 3b | 3b | ||||
F | Salmo macrostigma (including S.macedonicus 5353) | 1 | 0 | X | 1 | 1 | 4b | 4b | The name Salmo trutta macrostigma (or Salmo macrostigma) has previously been used of many populations also in other regions around the Mediterranean, but in recent years those have been split into separate local species; | |||
F | Thymallus thymallus | 0 | 0 | Annex V | ||||||||
F | Umbra krameri | 1 | 0 | X | X | 1 | 1 | 4b | 4b | |||
F | Zingel streber | 1 | 0 | X | X | 2 | 2 | 4b | 4b | |||
F | Zingel zingel | 0 | 0 | Annex V | ||||||||
G | Isophya costata | 1 | 1 | X | 2 | n/a | 3b | n/a | Subotička peščara, Ivkovič | |||
G | Isophya stysi | 1 | 1 | ? | 5 | 5 | n/a | n/a | There is also some possibility to record Isophya stysi in the viccinity of Đerdap gorge; no data available | |||
G | Paracaloptenus caloptenoides | 1 | 1 | X | X | 3 | 2 | n/a | 3b | The least studied area in Serbia for this group is located in Central parts of the country, where only Paracaloptenus caloptenoides is to be expected (but maybe Saga pedo and Pholidoptera transsylvanica could also be recorded) | ||
G | Pholidoptera transsylvanica | 1 | 1 | ? | X | 3 | 2 | 3b | 3b | |||
G | Pyrgomorphula serbica | 1 | 1 | 1 | X | n/a | 1 | n/a | 4a | Tara NP | ||
G | Saga pedo | 0 | 1 | X | X | 3 | 2 | 4b | 4b | |||
G | Stenobothrus eurasius | 1 | 1 | ? | 5 | 5 | n/a | n/a | There is also some possibility to record Stenobothrus eurasius in north-western Serbia (Gakovo, Bački Breg, Stanišić) ; no data available | |||
G | Zeuneriana amplipennis | 1 | 1 | 1 | ? | X | 3 | n/a | 4a | n/a | around Sava & Danube | |
M | Canis aureus | Annex V | ||||||||||
M | Canis lupus | 1 | 1 | 1 | 1 | X | X | 1 | 1 | 4b | 3b | The species is given as a proposal for amendments to the Annexes of Habitats Directive - proposal for Annex V; + geographical restriction for Annex II & IV (The request for derogation (geographical restriction) refers only to a part of the wolf population lacated south of the Sava and Danube rivers. In the province of Vojvodina, the wolf will retain the status of a strictly protected species.) |
M | Castor fiber | 1 | 1 | X | X | 2 | 2 | 3b | 4a | |||
M | Cricetus cricetus | 0 | 1 | X | X | 2 | 2 | 4b | 4b | |||
M | Dinaromys bogdanovi | 1 | 1 | only in Kosovo I (Pavol) propose to exclude from the list | ||||||||
M | Dryomys nitedula | 0 | 1 | X | 5 | 2 | 0 | 4a | ||||
M | Felis sylvestris | 0 | 1 | 1 | X | X | 2 | 2 | 3b | 3b | The species is given as a proposal for amendments to the Annexes of Habitats Directive - proposal for Annex V; + geographical restriction for Annex IV (geographical restriction) refers only to a part of the wolf population lacated south of the Sava and Danube rivers. In the province of Vojvodina, the wolf will retain the status of a strictly protected species.) | |
M | Lutra lutra | 1 | 1 | X | X | 2 | 2 | 2 | 2 | |||
M | Lynx lynx (Lynx lynx balcanicus; Lynx lynx carpathicus) | 1 | 1 | ? SR | X | 1 | 1 | 0 | 4b | ? SR - PAN - Scientific reserve - needs further confirmation by field mapping (Deliblatska peščara/vršačke planine) | ||
M | Martes martes | Annex V | ||||||||||
M | Muscardinus avellanarius | 0 | 1 | X | X | 2 | 2 | 4a | 3a | |||
M | Mustela eversmanii | 1 | 1 | X | ? SR | 2 | 5 | 4b | 6 | ? SR - CON - Scientific reserve - needs further confirmation by field mapping | ||
M | Mustela lutreola | 1 | 1 | Ex | 1 | 1 | 0 | 0 | Ex- data missing from 1941 | |||
M | Mustela putorius | Annex V | ||||||||||
M | Rupicapra rupicapra balcanica | 1 | 1 | 1 | X | 1 | 2 | 0 | 4b | The species is given as a proposal for amendments to the Annexes of Habitats Directive - proposal for Annex V; + geographical restriction for Annex II & IV ? SR Alpine - it is confirmed only in Kosovo alpine region | ||
M | Sicista subtilis | 1 | 1 | X? | 2 | 1 | 4a | 0 | X? - PAN -missing recent data, only 1 literature data record from 1992 in Deliblatska peščara) | |||
M | Spermophilus citellus | 1 | 1 | X | X | 2 | 2 | 3b | 3b | |||
M | Ursus arctos | 1 | 1 | 1 | X? | X | 1 | 1 | 0 | 4b | X? - PAN - a few recent records of single specimens in Vojvodina | |
M | Vormela peregusna | 1 | 1 | X | 1 | 2 | 0 | 4b | ||||
Mo | Anisus vorticulus | 1 | 1 | 5 | 5 | 6 | 6 | |||||
Mo | Theodoxus transversalis | 1 | 1 | X | 2 | 2 | 4b | 4b | ||||
Mo | Trochulus striolatus (Discus defloratus) | 0 | 1 | ? | Species is present in Serbia and is originally listed under the name Discus defloratus in the Annex IV of the Habitats Directive. However Discus defloratus has been incorrectly described on the basis of single empty shell and is now considered as a species Trichia striolata or Trochulus striolatus. As such the taxa should still be legally protected within EU. Further discussion is recquired! | |||||||
Mo | Unio crassus | 1 | 1 | X | X | 2 | 2 | 4b | 4b | usual fish hosts: Cottus gobio, Phoxinus phoxinus, Leuciscus cephalus, Scardinuis erythrophthalmus, Gymnocephalus cernua a Perca fluviatilis | ||
Mo | Vertigo angustior | 1 | 0 | ? | ? | 5 | 5 | 6 | 6 | The species Vertigo angustior and Vertigo moulinsiana could be recorded in Serbia, with special attention for V. moulinsiana which is widely distributied in the neighbouring countries. Their distribution should be checked in the field by group experts. | ||
Mo | Vertigo moulinsiana | 1 | 0 | ? | ? | 5 | 5 | 6 | 6 | The species Vertigo angustior and Vertigo moulinsiana could be recorded in Serbia, with special attention for V. moulinsiana which is widely distributied in the neighbouring countries. Their distribution should be checked in the field by group experts. | ||
R | Ablepharus kitaibelii | 0 | 1 | X | X | 3 | 2 | 4b | 2 | |||
R | Algyroides nigropunctatus | 0 | 1 | likely only in Kosove proposed for exclusion from ref.list | ||||||||
R | Coluber caspius (Dolichophis caspius) | 0 | 1 | X | X | 2 | 2 | 4b (5 areas) | 2 | |||
R | Coluber najadum (Platyceps najadum) | 0 | 1 | X | 3 | 4b | ||||||
R | Coronella austriaca | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
R | Cyrtopodion kotschyi (Mediodactylus kotschyi) | 0 | 1 | likely only in Kosove, in entire Serbia only introduced populations proposed for exclusion from ref.list | ||||||||
R | Elaphe longissima (Zamenis longissimus) | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
R | Elaphe quatuorlineata | 1 | 1 | X | 3 | 4b | ||||||
R | Emys orbicularis | 1 | 1 | X | X | 2 | 2 | 2 | 2 | |||
R | Lacerta agilis | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
R | Lacerta viridis | 0 | 1 | X | X | 2 | 1 | 2 | 2 | |||
R | Natrix tessellata | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
R | Podarcis erhardii | 0 | 1 | X | 3 | 4b | ||||||
R | Podarcis muralis | 0 | 1 | X | X | 2 | 2 | 1 | 1 | |||
R | Podarcis taurica | 0 | 1 | X | X | 2 | 2 | 2 | 2 | |||
R | Testudo graeca | 1 | 1 | X | 3 | 4b | ||||||
R | Testudo hermanni | 1 | 1 | ? | X | 2 | 2 | |||||
R | Vipera ammodytes | 0 | 1 | ? | X | 2 | 2 | 4b | 1 | |||
R | Vipera berus bosniensis (Vipera berus) | 0 | 1 | 1 | X | X | 3 | 2 | 4b | 2 | The species is given as a proposal for amendments to the Annexes of Habitats Directive - proposal for Annex IV; | |
R | Vipera ursinii | 1 | 1 | X | 3 | 4b | new data record in Mokra gora (Mala natura 2020) | |||||
R | Zootoca vivipara pannonica (Lacerta vivipara pannonica) | 0 | 1 | ? | distribution map for subspecies pannonica is not available (no data available yet) |