20I0 Acrocephalus v BirdLife INTERNATIONAL letnik 31 volume 31 številka 147 number 147 strani 175-301 pages 175-301 Impresum / Impresum Acrocephalus glasilo Društva za opazovanje in proučevanje ptic Slovenije Journal of DOPPS - BirdLife Slovenia ISSN 0351-2851 Izdajatelj in lastnik / Published and owned by: Društvo za opazovanje in proučevanje ptic Slovenije (DOPPS - BirdLife Slovenia), p.p. 2990, SI-1001 Ljubljana, Slovenija Oddaja rokopisov / Manuscript submision: DOPPS - BirdLife Slovenia, p.p. 2990, SI-1001 Ljubljana, Slovenija e-mail: luka.bozic@dopps.si Glavni urednik / Editor-in-Chief: Luka Božič e-mail: luka.bozic@dopps.si So urednik / Associate Editor: Dare Šere, e-mail: dsere@pms-lj.si (Iz ornitološke beležnice / From the ornithological notebook) Tehnični urednik / Technical Editor: Andrej Figelj, e-mail: andrej.figelj@dopps.si Uredniški odbor / Editorial Board: doc. dr. Damijan Denac (SI) Janez Gregori (SI) dr. Bojidar Ivanov (BG) prof. dr. Franc Janžekovič (SI) dr. Primož Kmecl (SI) dr. Jelena Kralj (HR) prof. dr. Lovrenc Lipej (SI) dr. Gordan Lukač (HR) Tomaž Mihelič (SI) dr. Roger H. Pain (GB) dr. Nikolai V. Petkov (BG) prof. dr. Jenö J. Purger (HU) dr. Peter Sackl (AT) dr. Martin Schneider-Jacoby (DE) doc. dr. Peter Skoberne (SI) dr. Tomi Trilar (SI) prof. dr. Peter Trontelj (SI) Marko Tucakov (RS) doc. dr. Al Vrezec (SI) Lektor in prevajalec / Language editor and translator: Henrik Ciglič Oblikovanje / Design: Jasna Andrič Prelom / Typesetting: Tadeja Smrtnik, Camera d.o.o. Tisk / Print: Schwarz d.o.o. Naklada / Circulation: 1500 izvodov / copies Izhajanje in naročnina: V letniku izidejo 4 številke. Letna naročnina za ustanove je 124,00 EUR, za posameznike 50,00 EUR. Annual publications and membership subscription (abroad): One volume comprises 4 numbers. Annual subscription is 124,00 EUR for institutions and organisations, and 50,00 EUR for individuals. Vaš kontakt za naročnino / Your contact for subscription: DOPPS - BirdLife Slovenia (za Acrocephalus) p.p. 2990 SI-1001 Ljubljana, Slovenija tel.: +386 1 4265875, fax: +386 1 4251181 e-mail: dopps@dopps.si Poslovni račun: SI5602018-0018257011 International Girobank: Nova Ljubljanska banka No. SI5602018-0018257011 Sofinancer / Co-financed by: Javna agencija za knjigo Republike Slovenije / Slovenian Book Agency Revija je indeksirana / the journal is indexed in: AQUATIC SCIENCES AND FISHERIES ABSTRACTS, BIOSIS PREVIEWS, BOSTAO SPA SERIALS, COBIB, DLIB.SI, ORNITHOLOGICAL WORLDWIDE LITERATURE, ORNITOLOGISCHE SCHRIFTENSCHAU, RAPTOR INFORMATION SYSTEM, ZOOLOGICAL RECORDS Published by: V E R S I T A © Revija, vsi v njej objavljeni prispevki, tabele, grafikoni in skice so avtorsko zavarovani. Za rabo, ki jo zakon o avtorskih pravicah izrecno ne dopušča, je potrebno soglasje izdajatelja. To velja posebej za razmnoževanje (kopiranje), obdelavo podatkov, prevajanje, shranjevanje na mikrofilme in shranjevanje in obdelavo v elektronskih sistemih. Dovoljeno je kopiranje za osebno rabo v raziskavah in študijah, kritiko in v preglednih delih. Mnenje avtorjev ni nujno mnenje uredništva. Partner: BirdLife International Revijo so omogočili: družba Mobitel, sponzor društva Grand Hotel Union, Prirodoslovni muzej Slovenije, donator ww Ilustracija na naslovnici / Front page; egiptovski jastreb / Egyptian Vulture risba / drawing: Jurij Mikuletič non percnopterus Ilustracija v uvodniku / Editorial page: južna postovka / Lesser Kestrel Falco naumanni risba / drawing: Jurij Mikuletič A Milestone on the Road to Natura 2000 Mejnik na poti k Naturi 2000 The publication "Important Bird Areas of Macedonia: Sites of Global and European Importance" provides a fascinating insight into the natural and cultural heritage of the country. The approved list of sites now includes a wide variety of landscapes hosting bird species that have become rare or threatened in many parts of Europe. Very important is the fact that only about 21% of the national protected area network overlaps the Important Bird Areas of Macedonia. Now an assessment of the natural assets of Macedonia is available for the first time, based on a systematic approach using the international criteria developed by BirdLife International for the selection of sites under the EU Birds Directive. The first results indicate where the country hosts areas of European and even global importance, where urgent conservation measures are needed, and are excellent guidelines for the rural development and tourism. A wide range of political commitments within the European Union is aimed at preserving ecosystems and biodiversity, with various species protection provisions as well as Special Protection Areas (SPAs) identified under the Birds Directive and Sites of Community Importance (SCIs) identified under the Habitats Directive, both incorporated into the Natura 2000 (N2000) network. The publication of the "Important Bird Areas of Macedonia" prepared by the Macedonian Ecological Society (MES) as a national representative of the BirdLife Internationals partnership is the first systematic assessment of Macedonia's sites based on the internationally recognized criteria to implement the Birds Directive. However, the complete identification of IBAs of EU importance (application of C criteria) will still need to follow in the future to fully comply with provisions of the Birds Directive. BirdLife's Important Bird Area (IBA) program is remarkable for the valuable -and largely unpaid — contribution it makes to the fulfilment of EU objectives: - Birds are the only pillar of N2000 for which a Europe-wide inventory based on the findings of an independent NGO network, the IBAs, exists. The European Commission makes active use of BirdLife Internationals publications in its evaluation of the completeness of national proposals for SPAs. - In practice, the N2000 network is defined, to a large extent, by IBAs. In many regions, SPAs and SCIs overlap, with birds serving as conspicuous indicators of rare and threatened habitats from remote coastal islands to the peaks of the Alps. Despite a joint database, the European Commmission is currently unable to report on the total size of the N2000 network in Europe (see N2000 Barometer1). Numerous sites have been designated both as SPAs and SCIs, making an entirely objective assessment of BirdLife's contribution impossible. Nevertheless, it is clear that IBAs play a key role in the establishment of national and European ecological networks. Back to Macedonia: quite striking is the fact that only about 21% of the IBAs cited here overlap the existing protected areas of the country. However, the effective implementation of the Birds Directive requires full, clear and precise transposition of sites by Member States. For countries such as Macedonia, the process of defining the IBAs is an excellent way to prepare the accession and to prevent degradation of the most important habitats. While Article 17 of the Habitats Directive requires Member States to report every six years on the progress made with the implementation of the Directive, it is important to start the preparation of the N2000 network in those countries, which have not achieved membership yet2. The publication has been prepared with great care and is based on data collected via extensive field work. While it provides relatively complete coverage of birds of prey and waterbirds, smaller songbirds and forest species are underrepresented — a significant shortcoming, given Macedonia's large tracts of forest. It will be the task of a later version to incorporate more data, based on line transects or other estimates. Birdwatchers visiting the country are encouraged to report their sightings to the MES or to offer their skills to evaluate the large forests, for example along the Macedonian part of the European Green Belt (Riecken 2010). In addition to mountains and wetlands, the new IBA publication includes areas of countryside such as the steppe-like habitats near the Bregalnica River (MK020), the huge plains of Pelagonia (MK012) and Ovče Pole (MK019). It is important that these sites of European importance become better known and that ways be found to preserve their functioning as habitats and support sustainable agriculture. The traditional large scale pasturing is one of the important land-use systems, which will need special attention to maintain and improve the conservations status of birds and many other species living on the sites (compare Schneider-Jacoby & Broxham 2010). The cultural landscape with its avifauna, including several species of highly threatened birds of prey, is a great asset of Macedonia. However, several of the species cited here, such as the Egyptian Vulture Neophron percnopterus and Lesser Kestrel Falco naumanni, no longer have a favourable conservation status in Macedonia, so that it will be not enough to promote the sites as IBAs and future N2000. Conservation will require restoration projects and continued sustainable management — that is, effective lobbying. Projects such as drainage of the Pelagonian marshes, performed in "Yugoslav times" without an environmental assessment, need to be re-evaluated before old drainage and irrigation systems are re-established. Only a proper assessment based on indicators and the natural potential will find solutions that improve the conservation status, for instance the restoration of the lost wetlands of the Crna Reka marshes (compare Thönen 2006, Stumberger & Schneider-Jacoby 2006). Achieving a favourable conservation status for species of global and European importance is a daunting task for any country. "Important Bird Areas of Macedonia" will aid Macedonia in complying with the Birds and Habitats Directives and implementing N2000 in its forthcoming European perspective. The publication highlights potential conflicts arising from infrastructure development and will help to foster ecologically sustainable rural development. Last but not least, it is an interesting reading that will raise the country's profile as a destination for birdwatching and eco-tourism. It provides fascinating insight into the country's natural and cultural heritage detailing a wide variety of habitats with many birds that are rare elsewhere in Europe (compare Schwaderer & Spangenberg 2009). *** Publikacija "Mednarodno pomembna območja za ptice globalnega in evropskega pomena v Makedoniji" daje nadvse zanimiv vpogled v naravno in kulturno dediščino te države. Potrjeni seznam območij zdaj zajema širok izbor krajin, v katerih živijo tudi ptičje vrste, ki so v mnogih delih Evrope že postale redke ali ogrožene. Nadvse pomembno je dejstvo, da se samo 21 % nacionalne mreže zavarovanih območij prekriva z mednarodno pomembnimi območji za ptice v Makedoniji. S tem delom je prvič na voljo ocena naravnih vrednot v Makedoniji, sloneča na sistematskem pristopu z uporabo mednarodnih kriterijev, ki jih je organizacija BirdLife International razvila za izbor območij v okviru evropske Ptičje direktive. Prvi rezultati zajemajo seznam območij evropskega in celo globalnega pomena, katere je treba zavarovati z nujnimi naravovarstvenimi ukrepi, hkrati pa so tudi izvrstne smernice za razvoj podeželja in turizem. Namen različnih političnih odločitev, ki jih je sprejela in se jim zavezala Evropska unij a, j e tudi ohraniti ekosisteme in biotsko pestrost z ukrepi varovanj a različnih vrst, kot tudi s posebnimi območji varstva (SPA), opredeljenimi v okviru Ptičje direktive, in posebnimi ohranitvenimi območji (SCI), opredeljenimi v okviru Habitatne direktive, obojimi vključenimi v omrežje Natura 2000 (N2000). Publikacija »Mednarodno pomembna območja za ptice globalnega in evropskega pomena v Makedoniji«, ki jo je pripravilo Makedonsko ekološko društvo (MES) kot nacionalni predstavnik partnerstva organizacije BirdLife International, je prvi sistematičen popis makedonskih območij, ki sloni na mednarodno priznanih kriterijih za uresničevanje Ptičje direktive. Toda da bi bila v celoti izpolnjena določila te direktive, bo v prihodnosti potrebna tudi popolna opredelitev IBA-jev pomembnih na nivoju EU z uporabo kriterijev C. Program BirdLifeovih mednarodno pomembnih območij za ptice (IBA) je izredno pomemben zaradi dragocenega — in v precejšnji meri neplačanega — prispevka k izpolnjevanju naslednjih ciljev EU: — Ptice so edini steber N2000, za katerega obstaja vseevropski popis območij, IBA-jev, sloneč na ugotovitvah mreže neodvisnih nevladnih organizacij. V svojih ocenah ustreznosti nacionalnih predlogov za določitev SPA-jev se Evropska komisija zanaša prav na publikacije organizacije BirdLife International. - V praksi N2000 v veliki meri opredeljujejo IBA-ji. V mnogih regijah se SPA-ji in SCI-ji prekrivajo, pri čemer se ptice uporabljajo kot jasni kazalci redkih in ogroženih habitatov vse od oddaljenih otokov do alpskih vrhov. Kljub skupni podatkovni bazi je Evropska komisija trenutno nezmožna poročati o skupni velikosti omrežja N2000 v Evropi (glej N2000 Barometer1). Mnoga območja so bila opredeljena kot SPA-ji in SCI-ji hkrati, kar pomeni, da ni mogoče popolnoma objektivno oceniti prispevka organizacije BirdLife International. Pa vendar je jasno, da IBA-ji igrajo ključno vlogo pri osnovanju nacionalnega in evropskega omrežja varstvenih območij. Vrnimo se k Makedoniji. V oči bode dejstvo, da se le 21 % IBA-jev, navedenih v tej publikaciji, prekriva z obstoječimi zavarovanimi območji v državi. Pa vendar učinkovita uresničitev Ptičje direktive terja poln, jasen in natančen prenos območij s strani držav članic EU. Za državo, kakršna je Makedonija, je proces določanja IBA-jev izvrstna priprava za pristop k EU in preprečevanje degradacije najpomembnejših habitatov. Medtem ko 17. člen Habitatne direktive zahteva od držav članic EU, da vsakih šest let poročajo o napredku v uresničevanju Direktive, je pomembno, da se priprave mreže N2000 lotijo v državah, ki še niso članice EU2. Pričujoča publikacija, ki je bila pripravljena nadvse skrbno, sloni na podatkih, zbranih med intenzivnim terenskim delom. Toda medtem ko razmeroma celostno pokriva ujede in vodne ptice, manjše ptice pevke in gozdne ptice niso predstavljene v zadostni meri, kar je glede na velike gozdne površine v tej državi precejšnja slabost. V poznejših različicah publikacije bo torej vanjo treba vključiti več podatkov, temelječih na linijskih transektih ali drugih ocenah. Opazovalci ptic, ki obiskujejo to državo, so zato vljudno vabljeni, da poročajo o svojih opažanjih Makedonskemu ekološkemu društvu ali pa da svoje znanje ponudijo pri vrednotenju velikih gozdov, na primer vzdolž makedonskega dela Evropskega zelenega pasu (Riecken 2010). Nova publikacija o makedonskih IBA-jih poleg gora in mokrišč vključuje stepam podobne habitate v bližini reke Bregalnice (MK020), prostrano Pelagonsko nižino (MK012) in Ovče Pole (MK019). Pomembno je, da ta območja evropske varstvene pozornosti postanejo bolje znana in da se najdejo načini, kako ohraniti njihovo delovanje kot habitatov in podpreti trajnostno kmetijstvo v njih. Zelo razvito tradicionalno pašništvo je eno izmed pomembnih sistemov rabe tal, ki mu je treba nameniti posebno pozornost, če želimo ohraniti in izboljšati varstveni status ptic in mnogih drugih vrst, ki živijo na tem območju (primerjaj Schneider-Jacoby & Broxham 2010). Kulturna krajina s svojo avifavno, ki vključuje več močno ogroženih ujed, je vsekakor velika vrednota Makedonije. Pa vendar že nekaj vrst, navedenih v tej publikaciji, na primer egiptovski jastreb Neophronpercnopterus in južna postovka Falco naumanni, v Makedoniji nima več ugodnega varstvenega statusa, kar pomeni, da promocija območij kot IBA-je in bodoča N2000, ne bo dovolj. Naravovarstvo bo terjalo pripravo projektov za ohranitev vrst in kontinuirano trajnostno upravljanje — se pravi učinkovito lobiranje. Projekte, kot je osuševanje pelagonskih močvirij, česar so se lotili v "jugoslovanskih časih" brez kakršne koli presoje vplivov, je treba oceniti na novo, in sicer še preden se ponovno uvedejo kakršni koli osuševalni in namakalni sistemi. Rešitve, ki bodo izboljšale varstveni status območij, na primer obnovitev tako rekoč izgubljenih močvirij Crne Reke (primerjaj Thönen 2006, Stumberger & Schneider-Jacoby 2006), bo prinesla le ustrezna ocena, temelječa na kazalcih in naravnih potencialih območij. Doseči ugoden varstveni status vrst globalne in evropske varstvene pozornosti je zelo težka naloga za vsako državo. Publikacija "Mednarodno pomembna območja za ptice v Makedoniji" bo pomagala tej državi, da izpolnjuje Ptičjo in Habitatno direktivo pri uresničevanju N2000 v njeni prihajajoči evropski perspektivi. Publikacija opozarja na potencialne konflikte, izvirajoče iz razvoja infrastrukture, in bo vsekakor pomagala pri pospeševanju trajnostnega razvoja podeželja. Nenazadnje pa je tudi zanimivo branje, ki bo izboljšalo podobo te države kot destinacije za opazovanje ptic in ekoturizem. S podrobnim orisom zelo različnih habitatov in ptic, ki so že zelo redke drugod po Evropi (primerjaj Schwaderer & Spangenberg 2009), pa zagotavlja tudi zelo zanimiv vpogled v makedonsko naravno in kulturno dediščino. Martin Schneider-Jacoby Project Manager at the EuroNatur / Projektni vodja pri organizaciji EuroNatur, e-mail: martin.schneider-jacoby@euronatur.org 1 http://ec.europa.eu/enviropnment/nature/natura2000/barometer/index_en.htm 2 Macedonia was granted official candidate country status for the accession to the EU in December 2005/ Makedonija je decembra 2005 dobila uradni status države kandidatke za ~lanstvo v EU References / Literatura Riecken, U. (2010): 20 years of Green Belt — Borders separate. Nature unites! pp. 27—31 In: Denac, D., Schneider-Jacoby, M. & Stumberger, B. (eds.): Adriatic Flyway — closing the gap in bird conservation. — EuroNatur, Radolfzell. Schneider-Jacoby, M. & Broxham, E. (2010): ELBARN Area Action Plan South East Europe — SAVE & EuroNatur, Radolfzell. — [http://www.elbarn.net/Elbarn/ Portals/0/Basics-ELBARN/Elbarn%20AAP_SEE. pdf], 9/12/2011. Schwaderer, G. & Spangenberg, A. (2009): EuroNatur Reiseführer Prespa - Ohrid -Region. — EuroNatur Service, Radolfzell. Stumberger, B. & Schneider-Jacoby, M. (2006): Pelagonien (Mazedonien) einst und heute (2). — Ornis 3: 12—14. Thönen W. (2006): Pelagonien (Mazedonien) einst und heute (1). — Ornis 3: 10—11. Important Bird Areas in Macedonia: Sites of Global and European Importance Mednarodno pomembna območja za ptice globalnega in evropskega pomena v Makedoniji Metodija Velevski1, Ben Hallmann2, Bratislav Grubač3, Tome Lisičanec4, Emilian Stoynov5, Emanuel Lisičanec4, Vasko Avukatov6, Luka Božič7 & Borut Stumberger8 1 Macedonian Ecological Society, P.O. Box 162, MK-1000 Skopje, Macedonia, e-mail: velevski@mes.org.mk 2 GR-40008 Rapsani, Greece, e-mail: benhallmann@gmail.com 3 Institute for Nature Protection of Serbia, Voždova 14, RS-18000 Niš, Serbia, e-mail: grubacbratislav@gmail.com 4 Aquila Nature Conservation Association, Belasica 3, MK-1400 Kavadarci, Macedonia, e-mail: e.lisichanets@gmail.com 5 Fund for Wild Flora and Fauna, BG-2700 Blagoevgrad, P.O. Box 78, Bulgaria, e-mail: pirin@fwff.org 6 Macedonian Ecological Society, P.O. Box 162, MK-1000 Skopje, Macedonia, e-mail: avukatov@mes.org.mk 7 DOPPS - BirdLife Slovenia, Kamenškova 18, SI-2000 Maribor, Slovenia, e-mail: luka.bozic@dopps.si 8 EuroNatur, Konstanzer Str. 22, D-78315 Radolfzell, Germany, e-mail: stumberger@siol.net Identification of the Important Bird Areas (IBAs) is an initiative implemented by BirdLife International at the global level, aiming to conserve a network of sites that are particularly important for the conservation of birds. With the changed conservation status of some species and increased information on the distribution and population sizes of birds in Macedonia in general, a revision of the IBA network was needed to update previous inventories for this country, published in 1989 and 2000. As the bird fauna of the Republic of Macedonia ranks among the least known in Europe, and as data on many species, notably passerines, are still largely missing, the inventory is mainly based on some threatened or rare birds of prey and a few other larger species, yet characteristic of the Macedonian landscape. Data used were collected in the course of different dedicated studies and projects carried out after 2000. Out of 314 species so far registered in Macedonia, 114 regularly occurring species have currently unfavourable conservation status in Europe, 84 of which breed or possibly breed in the country. Several criteria for the selection of IBAs of global (A criterion) and European importance (B criterion) developed by BirdLife International were used for sites selection, taking into consideration species of global conservation concern (A1), biome-restricted species (A3), important congregations (A4, B1) and species with an unfavourable conservation status (B2) or concentrated (B3) in Europe. Species of global conservation concern used for site identification include the Egyptian Vulture Neophron percnopterus, considered Endangered (EN) at the global level according to the latest IUCN Red List of Threatened Species, Dalmatian Pelican Pelecanus crispus and Imperial Eagle Aquila heliaca (both Vulnerable — VU), and Roller Coracias garrulus and Semicollared Flycatcher Ficedula semitorquata (both Near Threatened — NT). Furthermore, species assemblages characteristic as occurring mostly or entirely within a Eurasian high-montane or Mediterranean biome are found in Macedonia. Important congregations of non-breeding waterbirds with at least 1% of global or biogeographic populations of individual species occur on all three large lakes in the country, some of them (e.g. Dalmatian Pelican, Red-crested Pochard Netta rufina) in very large numbers, surpassing the 1% threshold by more than tenfold. In total, 25 species regularly occurring in the breeding season, for which the site protection approach is thought to be appropriate in Macedonia, were used for the selection of sites of European importance. Site boundaries were drawn following distinct natural features or isohypses to include breeding sites and foraging areas of triggering species, and, for Imperial Eagle and Egyptian Vulture also former breeding sites back to 1991, taking into consideration their habitat requirements, land-use and management needs. The resulting IBA list numbers 24 sites, covering 6,907 km2 or 26.9% of the entire territory of Macedonia: (1) Šar Planina Mountain, (2) River Radika Catchment, (3) Lake Ohrid, (4) Lake Prespa, (5) Demir Kapija Gorge, (6) Lake Dojran, (7) Zletovska River Valley, (8) Tikveš Region, (9) Pčinja - Petrošnica - Kriva Reka Rivers, (10) Preod - Gjugjance, (11) Osogovo Mountains, (12) Jakupica Mountain, (13) Taor Gorge, (14) Ovče Pole, (15) Topolka - Babuna - Bregalnica Rivers, (16) Gradsko - Rosoman - Negotino, (17) Lake Mantovo and Kriva Lakavica River, (18) Raec River Valley, (19) Pelagonia, (20) Mariovo, (21) Lake Tikveš, (22) Bošavija, (23) Kočani Rice Fields, and (24) Lower Vardar. With the exception of three sites occupying the highest parts of the large mountain massifs in NW and central parts of Macedonia, and the lakes Ohrid and Prespa, sites are concentrated mostly in central hilly and lowland parts of the country, comprising breeding areas of species of global conservation concern. The percentage of territory covered by the IBAs in Macedonia is relatively high compared to the total European average but comparable to several countries in SE parts of Europe. The size of separate IBAs ranges from 25 km2 (Taor Gorge) to 1,136 km2 (Pelagonia) and number of triggering species per site from one (Bošavija, Kočani Rice Fields) to 17 (Pčinja - Petrošnica - Kriva Reka Rivers). 22 sites trigger some of the criteria of global importance — three sites (Lakes Ohrid, Prespa and Dojran) meet A4 criterion, eight sites hold significant populations of species characteristic of the Mediterranean biome, while three other sites sustain significant populations characteristic of the European high-montane biome. Species of global conservation concern are included as follows: Egyptian Vulture on 13 sites, Imperial Eagle on 7, Dalmatian Pelican and Saker Falcon Falco cherrugon 2, Ferruginous Duck Aythya nyroca on 3, Roller Coraciasgarrulus on 10, Red-footed Falcon Falco vespertinus on 3 sites, and Semi-collared Flycatcher on 1 site. Individual triggering species for sites of European importance are represented on 2-15 sites. The IBA network includes 80-100% of the national populations of the globally threatened species, while the coverage of other species vary between 5% and 100%, being over 40% in great majority of species. Non-irrigated arable land and transitional woodland-shrub are dominant land-cover types, jointly covering 32% of the total IBA surface area. Abandonment of traditional pastoral system, resulting in decrease of the livestock numbers and overgrowing as well as trapping, poisoning and poaching, are considered the most serious threats for triggering species, particularly the Egyptian Vulture and Imperial Eagle, being classified as high on no less than 11 sites, respectively. The national legal protection of the sites is incomplete, being either only partial or with inadequate conservation measures adopted, or, many sites still lack any form of legal protection. With about 21% of the National protected area network overlapping with the IBAs, the existing protected area system is thus insufficient for conservation of most priority species. Notably underrepresented are the regions in the lower parts of the country with the highest number of species of global conservation concern. Key words: Important Bird Areas, IBA identification, triggering species, population size, IBA criteria, species of global conservation concern, threats, Macedonia Ključne besede: Mednarodno pomembna območja za ptice, opredelitev IBA, kvalifikacijske vrste, velikost populacij, IBA kriteriji, vrste globalne varstvene pozornosti, dejavniki ogrožanja, Makedonija KayqHH 3ÖopoBH: 3HanajHH nogpanja 3a ^TH^H, HgeHTH$HKa^Hja Ha 3111 i, BHgoBH koh ra HcnojmyBaaT KpmepHyMHTe 3a 3nn, rojeMHHa Ha ^o^yJIa^Hja, KpHTepnyMH 3a ro6op Ha 31111, BHgoBH og rao6aneH urnepec 3a 3anyByBaae, 3aKaHH, MaKegoHHja 1. Introduction 1.1. IBA programme and its history in Macedonia Identification of the Important Bird Areas (hereinafter referred to as to "IBAs" ) is an initiative implemented by BirdLife International at the global level, aiming to conserve a network of sites that are particularly important for the conservation of birds, i.e. for globally threatened species, species of European conservation concern, for migratory species that congregate in high numbers, species unique for small regions (endemic species) and sites that support species assemblages highly representative of a distinct biome (Heath & Evans 2000). The first IBA inventory that covered Europe was published in 1989, and within, Macedonia was elaborated as a part of former Yugoslavia. At that time, B. Grubač compiled the data of the seven terrestrial sites, while the lakes were included on the basis of results from the mid-winter censuses in 1987 and 1988 (Grimmett & Jones 1989). At that time, 10 IBAs were identified (Table 1, Figure 1), with a total coverage of 2,709 km2 (ca. 10% of the territory of Macedonia). This list was partially revised in 2003, when three new IBAs were proposed by E. Stoynov and accepted by BirdLife International. Two of them (Rice Plantations of Bregalnica and Zletovska Rivers, MK012 and Tikveš, MK013) were proposed on the basis of A1 criterion, supporting populations of Lesser Kestrels Falco naumanni and/or Imperial Eagles Aquila heliaca, while the third (Bistrenci Fishpond, MK011) was already within the boundaries of the previously identified IBA Demir Kapija Gorge (MK008), and was proposed under criterion B1iv (assumed bottleneck for passage of > 5000 White Storks Ciconia ciconia). With the changed conservation status of some species (especially uplisting the Egyptian Vulture Neophron percnopterus and the Roller Coracias garrulus as Endangered and Near Threatened in 2007), and increased information on the distribution of these as well as other species (Lesser Kestrel, Imperial Eagle, etc.) in Macedonia, with a more accurate estimation of their populations, a revision of the IBA network was needed. 1.2. Bird fauna of Macedonia Bird fauna of the Republic of Macedonia is among the least known in Europe, which is particularly true regarding the knowledge on distribution and quantitative population estimations, as can be witnessed by the gaps in the Atlas of European Breeding Birds (Hagemeijer & Blair 1997) and some rather imprecise estimates (BirdLife International 2004). Although the territory presently covered by the country has been of interest of foreign ornithologists in the period before the First and Second World Wars, and several milestone publications have been published with data from that period (Gengler 1920, Stresemann 1921, Makatsch 1950), later studies (until 2000) have been mostly sporadic, short-term or localized in coverage. Notable exceptions are the works of Dimovski (1967), studying the fauna of birds in Skopje Valley in the 1955—1959 period and Micevski (1998 & 2003) for Lakes Prespa (1987—1997) and Ohrid (1988—2000). Quantitative information on bird numbers and densities is also rare — in his papers, Dimovski (1967, 1971A & 1971B) provides information on the frequencies of findings of the species he had registered and their relative abundance only. The first and so far the only quantitative study of the terrestrial bird communities has been performed on Mt Galičica in the 1985—1989 period (Micevski 1990), while precise figures for the wintering populations at the three large lakes (Ohrid, Prespa and Dojran) have been gathered during several mid-winter counts (e.g. Micevski 1991 & 1996, Fremuth et al. 2000). Situation has been similar when censuses of particular species are concerned — the only complete countrywide census being the White Stork census in 1958 (Jovetic 1960). Later, somewhat less thorough in coverage, have been the works on the Golden Eagle Aquila chrysaetos in the 1980—1985 period, Lanner Falcon Falco biarmicus (1980—1994) and Long-legged Buzzard Buteo rufinus (1980—1995) (Grubač 1986/87, Figure 1: Map of Important Bird Areas (IBAs) in Macedonia identified in 1989 (Grimmett & Jones 1989, Heath & Evans 2000) Slika 1: Zemljevid mednarodno pomembnih obmo~ij za ptice (IBA-jev) v Makedoniji, opredeljenih leta 1989 (Grimmett & Jones 1989, Heath & Evans 2000) Table 1: List of IBAs in Macedonia identified during the 1989 (Grimmett & Jones 1989) and 2000 inventories (Heath & Evans 2000). Surface areas were recalculated by the Macedonian Ecological Society since the GIS technology has become available. Tabela 1: Seznam makedonskih IBA-jev, opredeljenih med popisi leta 1989 (Grimmett & Jones 1989) in 2000 (Heath & Evans 2000). Povr{ine obmo~ij je na novo izra~unalo Makedonsko ekolo{ko dru{tvo s pomo~jo tehnologije GIS. IBA code/ IBA koda Site name / Ime območja Centroid coordinates/ Koordinate centroida Surface area/ Površina (km2) Surface area (recalculated)/ Površina (preračunana) (km2) MK001 Shara Mountain [parts of] 2I°00'E, 42°00'N 120.0 i59.5 MK002 Korab Mountain and Radika Gorge 2I°I5'E, 4I°45'N 500.0 65i.4 MK003 Babuna Gorge, Topolka Gorge, and Crn Kamen 2I°45'E, 4I°40'N 25.0 38.5 MK004 Bregalnica River 22°00'E, 4I°45'N 100.0 306.9 MK005 Lake Ohrid 20°45'E, 4I°07'N 251.0 246.1 MK006 Lake Prespa 2I°00'E, 40°49'N 189.2 196.3 MK007 Crna River Gorge 22°00'E, 4I°I9'N 400.0 504.4 MK008 Demir Kapija Gorge 22°I9'E, 4I°I9'N 80.0 i22.0 MK009 Kozhuf Mountain and Boshava River 22°IJ'E, 4I°I0'N 200.0 460.3 MK010 Lake Dojran 22°45'E, 4I°I2'N 42.0 23.8 Total / Skupaj 1,907.2 2,709.2 Figure 2: The relief, main waterbodies and settlements in Macedonia (from ESRI Data & Maps for ArcView 9.1.) Slika 2: Relief, glavna vodna telesa in naselja v Makedoniji (po ESRI Data & Maps for ArcView 9.1.) 1994 & 1999), Wallcreeper Tichodroma muraria (19802000) (Grubač 2001) and vultures (1980-1997) (e.g. Grubač 1989 & 1997). The checklist of birds of Macedonia lists 314 species (Micevski 2002/2003), but since then information on two more species (Pallid Swift Apus pallidus, Vasic et al. 2009, and Great Black-headed Gull Larus ichthyaethus, Velevski & Saveljic 2010) has become available. Since 2009, updated checklists of birds of Macedonia and almost complete list of references for the country have been available online (Velevski 2011, Velevski & Štumberger 2011A & 2011B). Based on information compiled by E. Stoynov, B. Hallmann and M. Velevski, BirdLife international (2004) provides quantitative estimation for all breeding bird species regularly found in the country. However, in most cases these estimations are of poor quality and with very wide margins. For the few species for which more precise information is available, the information has been largely collected in the 2000-2003 period, mostly through different conservation projects (see Chapter 2.2.). After this publication, new or updated population estimates become available for few more species — Short-toed Eagle Circaetus gallicus (Velevski & Grubač 2007), Black Stork Ciconia nigra (Velevski et al. 2008), and the Lanner Falcon (Grubač & Velevski 2010). 114 regularly occurring species in Macedonia have currently unfavourable conservation status in Europe (SPEC 1 - nine species, SPEC 2 - 33 species, SPEC 3 — 72 species), 84 of which breed or possibly breed in the country. Out of them, one species, the Egyptian Vulture, is considered Endangered (EN), three (Dalmatian Pelican Pelecanus crispus, Imperial Eagle and Saker Falcon Falco cherrug) Vulnerable (VU), and five more (Ferruginous Duck Aythya nyroca, Red-footed Falcon Falco vespertinus, Black-tailed Godwit Limosa limosa, Roller and Semicollared Flycatcher Ficedula semitorquata) Near Threatened (NT) at the global level (IUCN 2011). We have considered the Lesser Kestrel as Least Concern (LC) according to the latest assessment of its status (BirdLife International 2011). Figure 3: Main land use types, according to the CORINE Land Cover mapping, Level 1 (2006) Slika 3: Glavni tipi rabe tal po CORINE Land Cover mapping, Level 1 (2006) 2. Study area and methods 2.1. Study area Macedonia is small, land-locked country in the centre of the Balkan Peninsula, covering 25,713 km2 (ca. 0.25% of the European territory). The country can be roughly divided into the western mountainous region (Šar-Pindus Mountain Range, total of 141 peaks higher than 2,000 m a.s.l.), central lowland region (mostly the Vardar River Valley, 80-300 m a.s.l., Pelagonia Plain, 650 m a.s.l., Ovče Pole Plain, 350 m a.s.l.), and eastern mountain (Rhodopean) region (only three peaks above 2,000 m altitude). Large mountainous regions are also found in the central part of the country (20 peaks above 2,000 m altitude) and in the southern parts (12 peaks above 2,000 m altitude), with ridges forming part of the borderline with Greece. Most of the country surface (44.1%) ranges at altitudes between 500-1,000 m a.s.l. (State Statistical Office of the Republic of Macedonia 2011) (Figure 2). Two large tectonic lakes, Ohrid (shared with Albania) and Prespa (shared with Albania and Greece), define the SW corner of the country, while the third natural lake (Lake Dojran) is located in the SE corner, on the borderline with Greece. The longest river is the Vardar (301 km), its longest left tributary the Bregalnica (225 km), and the longest right tributary the Crna Reka (207 km) (Gaševski 1978). In 2010, forests occupied 36.9% of the territory (broadleaved forests being dominant with 21.4%, while mixed forests comprise 12.3% and conifer forests only 3.3%), 19.8% were cultivated land and 23.8% pastures (State Statistical Office of the Republic of Macedonia 2011) (Figure 3). Large portions in the central part of the country are of steppe-like character. The climate is sub-Mediterranean in the southern lowland parts (average annual temperatures 13.8-14.5 oC), continental throughout most of the country and mountainous above roughly 1,500 m a.s.l. altitude (with annual averages from -0.6 to 8.7 oC). The average annual precipitation is 742 mm, ranging from 471 mm at Ovče Pole Plain (Central Macedonia) Table 2: Criteria for the selection of Important Bird Areas of global and European importance (after Heath & Evans 2000). Criteria denoted in bold were used for sites selection in Macedonia. Tabela 2: Kriteriji za izbor IBA-jev globalnega in evropskega pomena (po Heath & Evans 2000). Kriteriji v mastnem tisku so bili uporabljeni za izbor obmo~ij v Makedoniji. Category / Kategorija Criteria / Kriterij A criteria — Important Bird Areas of global importance A1. Species of global conservation concern A2. Restricted-range species A3. Biome-restricted species A4. Congregations The site regularly holds significant numbers of a globally threatened species, or other species of global conservation concern. The site is known or thought to hold a significant component of the restricted-range species whose breeding distributions define an Endemic Bird Area (EBA) or Secondary Area (SA). The site is known or thought to hold a significant assemblage of the species whose distributions are largely or wholly confined to one biome. i) The site is known or thought to hold, on a regular basis, > 1% of a biogeographic population of a congregatory waterbird species. ii) The site is known or thought to hold, on a regular basis, > 1% of the global population of a congregatory seabird or terrestrial species. iii)The site is known or thought to hold, on a regular basis, > 20,000 waterbirds or > 10,000 pairs of seabirds of one or more species. iv) The site is known or thought to be a bottleneck site where at least 20,000 storks (Ciconiidae), raptors (Accipitriformes & Falconiformes) or cranes (Gruidae) regularly pass during spring or autumn migration. B criteria — Important Bird Areas of European importance B1. Congregations B2. Species with an unfavourable conservation status in Europe B3. Species with a favourable conservation status in Europe i) The site is known or thought to hold > 1% of a flyway or other distinct population of a waterbird species. ii) The site is known or thought to hold > 1% of a distinct population of a seabird species. iii)The site is known or thought to hold > 1% of a flyway or other distinct population of other congregatory species. iv) The site is a 'bottleneck' site where over 5,000 storks, or over 3,000 raptors or cranes regularly pass on spring or autumn migration. The site is one of the 'n' most important in the country for a species with an unfavourable conservation status in Europe (SPEC 2 & 3) and for which the site-protection approach is thought to be appropriate. The site is one of the 'n' most important in the country for a species with a favourable conservation status in Europe but concentrated in Europe (non-SPECE*) and for which the site-protection approach is thought to be appropriate. * Formerly referred to as SPEC 4 species but renamed to non-SPECE in BirdLife International (2004) to 1,096 mm at Mt Šar Planina (NW Macedonia) (Lazarevski 1993, State Statistical Office of the Republic of Macedonia 2011). Human population was 2,022,547 in 2002, with average density of 78.7 people/km2 mostly concentrated in the urban centres (25% in the capital Skopje). Currently, the population is employed mainly in industry and trade (41.5%), while agriculture, forestry and hunting jointly contribute to the employment rate with only 3% (State Statistical Office of the Republic of Macedonia 2011). However, agriculture as a secondary profession is common in rural centres. 2.2. Data collection Several different surveys and conservation projects have resulted in numerous precise distribution data and quantitative estimations for many species, that were used at identification of the IBAs in Macedonia. The present proposal is based on data mostly gathered in the 2002—2011 period, but where necessary, older information was used in order to fill in some gaps in our knowledge. Data on mountain IBAs were collected during the research camps organised by the Biology Students' Table 3: Species of global conservation concern, registered in Macedonia until 2011 with statuses and thresholds given. Denoted in bold are species for which identification of Important Bird Areas was considered possible under the A1 criterion. Tabela 3: Vrste globalne varstvene pozornosti, zabeležene v Makedoniji do leta 2011, z njihovim statusom in populacijskimi pragovi. Z mastnim tiskom so ozna~ene vrste, za katere je bila opredelitev IBA ocenjena kot mogo~a v okviru kriterija A1. Species / Vrsta IUCN 2011 Red List Category/ Kategorija Rdečega seznama Status in Macedonia/ Status v Makedoniji Threshold/ Populacijski prag Pelecanus crispus VU Resident, not breeding 30 ind. Anser erythropus* VU Vagrant? 15 ind. Branta ruficollis EN Vagrant Regular presence Marmaronetta angustirostris VU Extinct 15 ind. Aythya nyroca NT Resident, breeding 20 pairs Oxyura leucocephala EN Vagrant Regular presence Milvus milvus NT Vagrant 30 ind. Neophron percnopterus EN Migratory, breeding Regular presence Aegypius monachus NT Extinct 5 pairs Circus macrourus NT Vagrant 30 ind. Aquila clanga VU Vagrant 6 ind. Aquila heliaca VU Resident, breeding 2 pairs Falco vespertinus NT Migratory, possible breeding 30 ind. Falco cherrug VU Probable breeding 2 pairs Tetrax tetrax NT Extinct? 60 ind. Otis tarda VU Vagrant? 30 ind. Gallinago media NT Vagrant? 60 ind. Limosa limosa NT Migratory 60 ind. Numenius tenuirostris* CR Vagrant? 1 ind. Numenius arquata NT Migratory 60 ind. Coracias garrulus NT Migratory, breeding 10 pairs Acrocephalus paludicola VU Vagrant? 30 ind. Ficedula semitorquata NT Migratory, breeding 20 pairs * Species given as "possibly to be found in Macedonia as it has been found in neighbouring regions" in Matvejev & Vasic (1973) and as such transferred in the latest checklist (Micevski 2002/2003) "?" denotes uncertain status of the species IUCN Red List categories (only the following categories were applied): CR — Critically Endangered, E — Endangered, VU — Vulnerable, NT — Near Threatened Research Society, particularly for Šar Planina (19951998; Kajevska et al. 1996, Velevski et al. 2002a), Mt Bistra (Velevski et al. 2003B), Pelister (Velevski et al. 2003A), Jakupica (1997-1999; Velevski et al. 2002B, and in 2010 during the preparation of the Multipurpose Protected Area »Jasen« management plan by UNDP — United Nations Development Program and Exploring Society »Ursus speleos« from Skopje). Results from the inventory for the needs of the National Park »Mavrovo« management plan prepared by Oxfam Italia (Micevski 2010) have also been considered. Still unpublished data for other high-mountain regions gathered by M. Velevski in the 2002-2009 period during the projects implemented by the Biology Students' Research Society and the Macedonian Ecological Society were also available for the mountains of Korab, Jablanica, Kožuf, Nidže and Osogovo. Census of the Lesser Kestrel population in Pelagonia in 2002 (B. Stumberger & M. Velevski unpubl.) resulted with estimation of the population of not only this species, but also of the White Stork (Stumberger & Velevski 2002), Montagu's Harrier Circus pygargus, Jackdaw Corvus monedula and Roller. At the same time, a survey of the Lesser Kestrel colonies took place in other parts of Macedonia (Lisichanets et al. 2004). With the start of the Vulture Conservation Project in Macedonia in 2003, implemented by the Macedonian Ecological Society and Aquila Nature Conservation Association (formerly Fund for Wild Flora and Fauna — Macedonia), precise data were gathered on Table 4: Species in Macedonia occurring mostly or entirely within a particular biome (biome-restricted species), for which IBA identification was considered appropriate under A3 criterion Tabela 4: Vrste v Makedoniji, ki se pojavljajo ve~inoma ali v celoti znotraj dolo~enega bioma (na dolo~en biom vezane vrste) in za katere je bila opredelitev IBA ocenjena kot ustrezna v okviru kriterija A3 Biome / Biom Species / Vrsta Eurasian high-montane Prunella collaris Tichodroma muraria Pyrrhocorax graculus Montifringilla nivalis Mediterranean Alectoris graeca Oenanthe hispanica Hippolais olivetorum Sylvia cantillans Sylvia melanocephala Sitta neumayer Lanius nubicus Emberiza melanocephala population sizes of the Egyptian and Griffon Vultures Gypsfulvus, but data of good quality were also gathered for the Black Stork (Velevski et al. 2008), Lanner Falcon Falco biarmicus (Grubač & Velevski 2010), Short-toed Eagle (Velevski & Grubač 2008), Golden Eagle, Long-legged Buzzard and Eagle Owl Bubo bubo. The Imperial Eagle has also been partially covered with these surveys, with the special survey and monitoring of this species carried out by B. Hallmann, T. Lisičanec and E. Lisičanec in the 2003-2008 period. In 2010 and 2011, the Macedonian Ecological Society implemented mid-winter censuses at the three large lakes, Ohrid, Prespa and Dojran, together with several smaller sites. Hitherto no detailed surveys have been carried out for passerines, therefore quantitative population estimates for separate sites have rarely been possible. The surveys carried out by a group of Czech ornithologists (Skorpi'kova et al. 2006 & 2007) and the detailed information made available by them to the authors were of significant value in improving the estimation of populations and delineation of the boundaries of some sites. Finally, a census of White Stork was carried out in parts of Central and Eastern Macedonia by H. Heckenroth and J.-U. Heins (The Stork Foundation) during 2010 and 2011. As a result of the information available, compared to BirdLife International (2004), new national estimations were provided for several species (Appendix 1). 2.3. Criteria for IBA identification Several criteria for the selection of IBAs have been developed by BirdLife International (Heath & Evans 2000). According to them, the international importance of sites can be categorized at different geographical levels: global (A criterion), European (B criterion) and European Union (C criterion, used for the selection of sites under the EU Birds Directive not treated herein). Criteria for the selection of sites of global and European importance are summarized in Table 2. The methodology for identification of the IBAs presented in Heath & Evans (2000) was followed. The latest assessment of the Red List category (IUCN 2011) was used for the selection of species of global conservation concern. SPEC categories were after BirdLife International (2004), together with estimation of the European populations, except for the Lesser Kestrel, Roller, Egyptian Vulture and Semi-collared Flycatcher, where the data from the updated species action plans were used (Inigo et al. 2008, Kovacs et al. 2008, Georgiev & Iankov 2010, Inigo & Barov 2010). The following criteria were used for selection of IBAs in Macedonia: (1) A criteria: Important Bird Areas of global importance For identification of the sites of global importance under the criteriaA1 and A3, lists ofspecies potentially fulfilling these criteria were developed (Tables 3 & 4), and only the species regularly occurring in the country were taken into consideration. Under the A1 criterion, sites holding sufficient numbers of globally threatened (IUCN Red List categories CR, EN and VU) and Near Threatened (NT) species are selected. For Critically Endangered (CR) and Endangered (EN) species, their regular presence alone merits the site identification, while others should meet corresponding thresholds (Table 3) and be regularly present at a site. Thresholds were used after Heath & Evans (2000) updated with information from BirdLife International (I. Burfieldpers. comm.). Under the A3 criterion, representative sites, holding rich assemblages of biome-restricted species and reflecting the distribution of biome in the country are selected. Out of five biomes treated under this criterion in Europe, two occur in Macedonia - the Eurasian high-montane biome (with 10 characteristic bird species in Europe) and Mediterranean biome (21 characteristic species). The list of biome-restricted species occurring in Macedonia is given in Table 4. Table 5: Population estimates of non-breeding congregatory waterbirds in Macedonia in the 1988-2011 period. Species denoted in bold meet 1% threshold for criteria A4i and B1i on at least one site. Tabela 5: Ocene populacij negnezdečih vodnih ptic, ki se združujejo v jate, v Makedoniji v obdobju 1988-2011. Vrste, prikazane v mastnem tisku, zadovoljujejo enoodstotni populacijski prag za kriterija A4i in B1i v vsaj enem območju. Non-breeding Percentage of population MK population in 1% Species/ (ind.)/ Waterbird population/ MK / Odstotek treshold/ Vrsta Negnezdeča Populacija vodnih ptic populacije v popul. popul. MK (os.) MK (%) prag min max min max Gavia arctica 5 50 arctica < 0.1 < 0.1 3,750 Tachybaptus ruficollis 100 900 ruficollis < 0.1 0.2 4,000 Podiceps cristatus 400 5,700 Black Sea, Mediterranean 0.1 0.8 7,250 Podiceps nigricollis 100 5,700 Europe, N Africa < 0.1 2.7 2,200 Phalacrocorax carbo sinensis 100 1,200 Black Sea, Mediterranean < 0.1 0.3 4,000 Phalacrocorax pygmeus 20 3,500 SE Europe, Turkey < 0.1 5.0 700 Pelecanus onocrotalus* 200 550 Europe, W Asia 1.0 1.7 270 Pelecanus crispus* 300 1,000 Black Sea, Mediterranean 6.0 20.8 45 Cygnus olor 10 160 Black Sea < 0.1 0.4 450 Anas penelope 65 940 Black Sea, Mediterranean < 0.1 0.3 3,000 Anas strepera 10 100 Central Europe, Black Sea, Mediterranean < 0.1 0.1 1,100 Anas crecca 650 6,500 Black Sea, Mediterranean 0.1 0.6 10,600 Anas platyrhynchos 200 5,100 Black Sea, E Mediterranean < 0.1 0.3 20,000 Anas acuta 25 100 Black Sea, Mediterranean, W Africa < 0.1 < 0.1 7,500 Anas clypeata 15 100 Black Sea, Mediterranean, W Africa < 0.1 < 0.1 4,500 Netta rufina 550 7,000 Black Sea, E Mediterranean 1.9 23.7 320 Aythya ferina 300 10,500 Central Europe, Black Sea, Mediterranean < 0.1 1.1 10,000 Aythya nyroca 5 10 E Europe, E Mediterranean, Black Sea < 0.1 < 0.1 450 Aythya fuligula 300 18,500 Central Europe, Black Sea, Mediterranean < 0.1 2.6 7,000 Bucephala clangula 20 500 SE Europe, Adriatic < 0.1 0.3 2,000 Mergellus albellus 2 35 Black Sea, E Mediterranean < 0.1 0.1 350 Mergus merganser 2 22 Balkans 2.8 31.1 1 Fulica atra 20,000 81,000 Black Sea, Mediterranean 0.8 3.2 20,000 Larus ridibundus 100 1,600 E Europe < 0.1 0.1 13,000 Larus michahellis / cachinnans 20 1,400 michahellis / cachinnans < 0.1 0.2 20,000 Wintering populations, except * non-breeding population occurring in the reproductive period of the species. Waterbird population after Wetlands International (2006). For category A4, the site must meet at least one of the criteria given in Table 2. However, Birdlife International now treats A4i as 1% of the total global population (I. Burfield pers. comm.). We have used data from the winter waterbird censuses (Micevski 1991, Micevski 1996, Micevski & Schneider 1997, Micevski 1998, Fremuth et al. 2004, Wetlands International in litt.), unpublished results of the Macedonian Ecological Society from 2010 and 2011, and estimates of their respective global populations (Wetlands International 2006) for site identification under the A4i criterion. We have considered species qualifying under A4i only if it has met 1% of its total global population in at least one third of the mid-winter counts. Total numbers of waterbirds registered during the winter counts were used to test sites against A4iii criterion (> 20,000 waterbirds on regular basis). (2) B criteria: Important Bird Areas of European importance Several criteria for the identification of sites of European importance were considered suitable for Macedonia. We have considered species qualifying under Table 6: Species used for identification of Important Bird Areas under B2 and B3 criteria, with population estimates, percentage of European population in Macedonia, median of population size in IBAs confirmed under the B2 & B3 criteria in the World Bird/Biodiversity Database (WBDB) and thresholds used in Macedonia given Tabela 6: Vrste, uporabljene za opredelitev IBA-jev v okviru kriterijev B2 in B3, z ocenami njihovih populacij, odstotkom evropske populacije v Makedoniji, srednjo vrednostjo velikosti populacije v IBA-jih, potrjenih v okviru kriterijev B2 in B3 v World Bird/Biodiversity Database (WBDB), in s populacijskimi pragovi, uporabljenimi v Makedoniji Population MK/ Population Europe/ Percentage of Europe population in MK/ Odstotek evropske populacije v MK Max. No. of sites under B2 Median IBAs Europe / Srednja vrednost v evropskih IBA-jih (B2 & B3) B2&B3 thresholds Species / Vrsta SPEC Populacija MK Populacija Evropa & B3 / Največje št. območij v okviru B2 for MK/ Populacijski prag za MK min max min max (%) in B3 min max Falco naumanni i 1,500 2,500 29,900 34,500 6.0 10 95 100 20 Aquila heliaca i 30 40 850 1,400 3.2 5 3 4 2 Phalacrocorax pygmeus i 60 120 28,000 39,000 0.4 5 80 110 30 Aythya nyroca i 20 40 12,000 18,000 < O.I 5 25 40 10 Crex er ex i 50 150 1,300,000 2,000,000 < O.I 5 40 50 20 Alectoris graeea 2 2,000 5,000 40,000 78,000 5-7 10 60 100 50 Accipiter brevipes 2 40 100 3,200 7,700 i-3 5 8 12 3 Lanius nubicus 2 300 500 35,000 100,000 0.7 5 10 20 10 Ciconia ciconia 2 65 0 800 180,000 220,000 0.4 5 80 110 30 Coracias garrulus 2 200 400 55,000 117,000 0.4 5 20 35 10 Ciconia nigra 2 35 45 7,800 12,000 0.4 5 10 10 3 Lanius minor 2 2,000 5,000 620,000 1,500,000 0.3 5 30 60 30 Falco biarmicus 3 25 35 480 900 4-5 5 i 3 1-2 Circaetus gallicus 3 120 150 8,400 13,000 i-3 5 10 14 3 Monticola saxatilis 3 1,000 2,500 100,000 320,000 0,9 5 25 40 30 Buteo rufinus 3 80 120 8,700 15,000 0.9 5 8 10 4 Aquila chrysaetos 3 60 100 8,400 11,000 0.8 5 7 8 3 Neophron percnopterus 3 28 32 3,300 5,050 0.7 5 5 5 3 Bubo bubo 3 100 300 19,000 38,000 0.6 5 10 15 4 Burhinus oedicnemus 3 200 400 46,000 78,000 0.5 5 50 100 20 Monticola solitarius 3 400 1,000 120,000 260,000 0.4 5 15 30 20 Ixobrychus minutus 3 200 300 60,000 120,000 0.3 5 50 70 20 Riparia riparia 3 1,000 5,000 5,400,000 9,500,000 < O.I 5 10,000 10,000 1,000 Sternula albifrons 3 20 50 35,000 55,000 < O.I 5 70 120 20 Circus pygargus non-SPECE 100 140 35,000 65,000 0.2 5 20 45 20 Nadaljevanje tabele 6/ continuation of Table 6 Population estimates refer to breeding pairs after BirdLife International (2004), except Falco naumanni, Coraciasgarrulus, Neophronpercnopterus and Ficedula semitorquata, where data from the action plans were used (Inigo et al. 2008, Kovacs et al. 2008, Georgiev & Iankov 2010, Inigo & Barov 2010) SPEC — species of European conservation concern (SPEC 1 — European species of global conservation concern in Europe, i.e. classified as Critically Endangered, Endangered, Vulnerable, Near Threatened or Data Deficient under the IUCN Red List Criteria at a global level; SPEC 2 — species whose global populations are concentrated in Europe, and which have an Unfavourable conservation status in Europe; SPEC 3 — species whose global populations are not concentrated in Europe, but which have an Unfavourable conservation status in Europe; non-SPECE — species whose global populations are concentrated in Europe but which have a Favourable conservation status in Europe) (BirdLife International 2004) B1i only if it has met 1% threshold for the individual waterbird flyway population (Wetlands International 2006) in at least one third of the mid-winter counts (Table 5). For identification of the sites that meet B2 and B3 criteria, the following steps were followed for selection of the triggering species: — to have unfavourable conservation status in Europe (SPEC 1, 2 & 3) — B2, or favourable conservation status, but with more than 50% of their global range lying in Europe (non-SPECE) — B3 (BirdLife International 2004); — a site protection approach is thought to be appropriate in Macedonia; — to have national population of at least 0.5% of the European population or it was possible to identify IBAs according to Heath & Evans (2000) who state, "Also, for countries which hold less than 1% of the European population of a given species, or for countries which comprise less than 1% of the total land area of Europe (i.e. less than ca. 100,000 km2), sites may still be selected under this criterion if they support similar numbers of the species as sites in other countries, which meet this criterion in a standard fashion". Instead of minimal populations, we applied geometric means of the estimations due to low quality of the estimation data provided in BirdLife International (2004). A threshold of 1% of the national population size was used to identify the most important sites for these species, but for species the minimal population size of which has been estimated at under or close to 100 pairs, like Levant Sparrowhawk Accipiter brevipes, Black Stork, Lanner Falcon, Short-toed Eagle, Long-legged Buzzard and Eagle Owl, direct recommendations from BirdLife International, based on the data from already confirmed IBAs in the World Bird/Biodiversity Database (WBDB), were followed (I. Burfieldpers. comm.). For species where national population was up to 5% of European population, maximum of five IBAs were proposed, while for species where national population was 5—10% of European population, 10 IBAs at the most were proposed. Species used for identification of IBAs under these criteria are given in Table 6. Full list of species considered under B2 and B3 criteria is given in Appendix 1. 2.4. Other important bird species Species of global conservation concern found with populations not sufficient to meet A1 criterion, SPEC 2 and SPEC 3 species that have populations that would otherwise meet B2 criterion, but for which maximal number of sites (5 or 10) has already been proposed, or do not meet the threshold set, but are still considered to be of national importance for conservation due to their small populations or negative population trends have been identified as 'other important species' and are also presented in the site overviews. Also, species with significant percentages of their national populations (roughly > 50%) found at only a few sites were included in this group. 2.5. Boundaries, land cover and threats For delineation of the boundaries, ArcView 9.1 (ESRI 2005) was used. All known nesting locations of solitary pairs and colonies of the triggering species, with number of pairs in colonies were overlaid on 1 : 25,000 scale topographic maps used as background layer. Boundaries were drawn to include breeding sites, foraging areas, and, for Imperial Eagle and Egyptian Vulture only, former breeding sites (back to 1991) as much as possible and reasonable. Also, habitat requirements of the triggering species, land-use and management needs were considered. All boundaries were drawn following natural distinct features (ridges, valleys, roads), or, where this was impossible, isohypses were followed. The chapters "Site description" (see 3.2. Overview of sites) include descriptions of the borders in a manner that they can be easily identified on topographic 1 : 25,000 scale maps. Geographical and geological characteristics are presented, after Kolčakovski (2004 & 2008). Figure 4: Map of the IBAs identified in Macedonia Slika 4: Zemljevid IBA-jev, opredeljenih v Makedoniji Using data from CORINE Land Cover (EEA 2006), the percentage of land cover types according to the CORINE Land Cover, Level 3 was calculated for each site. However, only land cover types exceeding 5% of the total surface area of the site are presented in the tables, others being merged under the label "Others". The exceptions are small-scale land cover types of particular importance for the triggering species. The overall classification of the major CORINE land cover types found within IBA boundaries is given in Appendix 2. Threats were identified on the basis of threat list provided in the national Emerald Database (see Appendix 3). To quantify the importance of threats with regard to their actual or potential impact, the scoring method after Heath & Evans (2000) was used: (1) Effect of threat on the habitat (for habitat- related threats) — destruction 3 — rapid deterioration 2 — slow deterioration (scores) 1 (1) Expected/measured effect on threatened species (for bird-related threats) — majority of critical species are affected 3 — some critical species are affected 2 — only non-critical species are affected 1 (2) Spatial scale of the threat in relation to the IBA — affects the IBA as a whole 3 — affects a large part of the IBA but not critical sites for threatened species or a relatively small part of the IBA, which is important for threatened species 2 — affects a relatively small part of the IBA with no crucial site for threatened species 1 (3) Realization of the threat — threat already exists 3 — threat is planned with realization expected in short term 2 — threat is planned with realization expected in longer term 1 Table 7: List of IBAs identified in Macedonia with criteria used. Tabela 7: Seznam IBA-jev, opredeljenih v Makedoniji z uporabljenimi kriteriji IBA code/ IBA koda Site name (Macedonian)/ Ime območja (makedonsko) Site name (English)/ Ime območja (angleško) IBA Criteria/ IBA kriteriji MK001 Šar Planina Šar Planina Mountain A3, B2 MK002 Sliv na reka Radika Radika River Catchment A3, B2 MK005 Ohridsko Ezero Lake Ohrid A4iii, B1i, B2 MK006 Prespansko Ezero Lake Prespa A1, A4i , B1i, B2 MK008 Demirkapiska Klisura Demir Kapija Gorge A1, A3, B2 MK010 Dojransko Ezero Lake Dojran A1, A4i , B1i, B2 MK012 Dolina na Zletovska Reka Zletovska River Valley A1, B2 MK013 Tikveški region Tikveš Region A1, B2 MK014 Reka Pčinja - reka Petrošnica - Kriva Reka Pčinja - Petrošnica - Kriva Reka Rivers A1, A3, B2 MK015 Preod - Gjugjance Preod - Gjugjance A1, B2 MK016 Osogovski Planini Osogovo Mountains A1, B2 MK017 Jakupica Jakupica Mountain A3, B2 MK018 Taorska Klisura Taor Gorge A1, A3 MK019 Ovče Pole Ovče Pole A1, B2 MK020 Reka Topolka - reka Babuna - reka Bregalnica Topolka - Babuna - Bregalnica Rivers A1, A3, B2 MK021 Gradsko - Rosoman - Negotino Gradsko - Rosoman - Negotino A1, A3, B2 MK022 Mantovsko Ezero i reka Kriva Lakavica Lake Mantovo and Kriva Lakavica River A1, B2 MK023 Dolina na reka Raec Raec River Valley A1, A3, B2 MK024 Pelagonija Pelagonia A1, A4ii, B1iii, B2, B3 MK025 Mariovo Mariovo A1, A3, B2 MK026 Tikveško Ezero Lake Tikveš A1, A3, B2 MK027 Bošavija Bošavija A1 MK028 Kočanski orizovi polinja Kočani Rice Fields B2 MK029 Dolen tek na reka Vardar Lower Vardar B2 The combined level of the threat is calculated by summing up the values (1), (2) and (3). Threats can be classified into three groups according to the magnitude of the impact: high impact (scores 8 and 9), medium impact (scores 6 and 7) and low impact (scores 3, 4 and 5). Detailed calculation of threat scores is given in Appendix 4. 2.6. Data presentation Species data are presented in tables. The first column delineates the species' Latin name, while the second column presents the information on the status of species and season in which species meets IBA criteria after Heath & Evans (2000) (R = breeding resident, B = breeding visitor, W = wintering visitor, P = passage visitor, N = non-breeding visitor, and U = unknown). In the column "Year", the year of population estimation is given. When period is given, it is related to species population size change or fluctuation in the given period. Under "Population", estimation of the population size in pairs (unless stated in individuals) is given. In some cases, where no sufficient data existed to estimate the population size, qualitative abundance estimates according to Heath & Evans (2000) have been presented ("abundant" = encountered in large numbers in preferred habitat, "common" = encountered singly or in small numbers in preferred habitat, "frequent" = often, but not always, met in the preferred habitat, "uncommon" = encountered sporadically in preferred habitat, "rare" = rarely seen, usually less than 10 records, and "unknown" = not possible to assess abundance). Quality of the estimation is presented in the column "Acc." (Accuracy), where A = reliable, B = incomplete, C = poor (after Heath & Evans 2000). No data quality is given if population figures are not available. In the last column "Criteria", one or more criteria that the species meet at a particular site are given, with "?" indicating that the species probably meets the given criterion, but further research is needed to justify it. In the same column, "N" is used when a population is considered to be of national importance. Species meeting at least one IBA criterion on given site are denoted in bold. 3. Results 3.1. Sites The new IBA proposal lists 24 sites (Table 7, Figure 4), covering 6,907.35 km2 or 26.9% of the territory of Macedonia (Table 7). With the exception of the mountain ranges in the NE and central parts of Macedonia, and Lakes Ohrid and Prespa, sites are distributed mostly in the central lowland parts of the country (Pčinja-Vardar Valleys and Pelagonia Plain). The size of separate IBAs ranges from 25 km2 (Taor Gorge) to 1,136 km2 (Pelagonia), with relative coverage of the country between 0.1 and 4.4%. The number of triggering species per site ranges from one (Bošavija, Kočani Rice Fields) to 17 (Pčinja - Petrošnica - Kriva Reka Rivers). Some of these localities are partially or entirely under protection of the national legislation (Ohrid Lake, Prespa Lake, Dojran Lake, Tikveš Lake, Demir Kapija and Radika River Catchment), while others are partially or entirely included in the national Emerald Network (Osogovo Mt, Topolka - Babuna - Bregalnica Rivers, Taor Gorge, Jakupica Mt, Sar Planina Mt, Ovče Pole, Pelagonia and Mariovo). Non-irrigated arable land and transitional woodland-shrub are dominant land-cover types, covering 1,171.5 km2 (17 sites), and 1,017 km2 (23 sites) in total, respectively. The total coverage of agricultural areas is 3,282 km2 (47.5%) of IBAs. 3.2. Overview of the sites 3.2.1. Šar Planina Mountain Name in English: Šar Planina Mountain Name in Macedonian: Šar Planina (fflap n^aHHHa) IBA code: MK001 Criteria: A3, B2 Area: 43,418 ha Central coordinates: 20o49'18.96"E, 41o57'11.34"N Altitude: 640-2,748 m a.s.l. Administrative region(s): Tearce, Tetovo, Bogovinje, Vrapčište, Gostivar, Rostuše-Mavrovo Site description The site occupies southern and central parts of Šar Planina Mt, which is one of the largest mountains in Macedonia, situated in its NW corner, and whose Figure 5: Map of the IBA Šar Planina Mountain with its main features depicted Slika 5: Zemljevid IBA Šar Planina z glavnimi zna~ilnostmi obmo~ja ridge forms the borderline with Kosovo. The lower boundary of the site runs at ca. 1,200 m a.s.l, but at places descends to as low as 640 m a.s.l. To the south, the boundary follows the Cafa e Kadis and Adina Reka Rivers and the ridge between the peaks of Lera (2,194 m a.s.l.), Morava (2,147 m a.s.l.) and Mala Planina (1,798 m a.s.l.). To the NW, it reaches the peak of Peskovi (2,651 m a.s.l.) and the Bistrica River Valley, leaving ca. 12 km of the mountain ridge (not of high importance for the conservation of triggering species) outside the site. Compared to the boundaries from 1989 (site YU048, Grimmett & Jones 1989) and 2000 (site MK001, Heath & Evans 2000), the site coverage has expanded almost three times. The site adjoins the IBA "Šar-planina" (RS035) in Kosovo, Puzovic et al. (2009). Mountainous relief dominates, with the highest parts of the mountain (Titov Vrv 2,748 m a.s.l., Mal Turčin 2,702 m a.s.l., Kobilica 2,528 m a.s.l. etc.) well above 2,500 m altitude. Quite characteristic is the Pena River General information Table 8: List of triggering and other important bird species in the IBA Šar Planina Mountain Tabela 8: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Šar planina Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Prunella collaris B 2004 20-40 C A3 Tichodroma muraria B 2004 5-10 C A3 Pyrrhocorax graculus B 2005 100-200 C A3 Montifringilla nivalis B 2004 10-30 C A3 Aquila chrysaetos R 2003 3-4 B B2 Alectoris graeca R 2009 50-150 C B2 Crex crex B 20I0 20-50 C B2 Bubo bubo R 2007 5-I0 C B2 Pyrrhocorax pyrrhocorax B Common B2? Gyps fulvus N 2009 1-10 ind. C N Falco peregrinus R 2009 2-5 C N Eremophila alpestris balcanica B Common N Table 9: The main CORINE land cover types (Level 3) in the IBA Šar Planina Mountain Tabela 9: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v IBA Šar planina Code/ Koda CORINE land cover type/ tip pokrovnosti in rabe tal Coverage/ Pokrovnost (%) 311 Broad-leaved forest 24.2 321 Natural grasslands 56.1 322 Moors and heathland 4.3 324 Transitional woodland-shrub 7.9 Other 7.5 Valley with the cliffs at the locality called Lešnica. Other larger river valleys are Jelovjanska Reka, Mazdrača and (Tearska) Bistrica. Geologically dominant are Paleozoic metamorphic cliffs with carbonates. Pleistocene glacial relief is present in the highest parts. Most of the glacial lakes on Šar Planina Mt are within the boundaries of the site, among which is also Lake Bogovinsko, the largest glacial lake in Macedonia (Figure 5). Species The list for the entire mountain totals ca. 130 species (Melovski et al. 2010), which indicates that the area has not been studied thoroughly. The site is one of the five most important sites for the Golden Eagle (3—4 Table 10: The main threats to birds and their importance in the IBA Šar Planina Mountain Tabela 10: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Šar planina Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 141 Abandonment of pastoral systems high G. fulvus, P. graculus 160 General forestry management high forest species 960 Interspecific faunal relations high A. chrysaetos, B. bubo, G. fulvus 230 Hunting medium A. graeca 243 Trapping, poisoning, poaching medium A. chrysaetos, G. fulvus 501 Paths, tracks, cycling tracks medium A. chrysaetos, G. fulvus 530 Improved access to site medium A. chrysaetos, G. fulvus 167 Forest exploitation without replanting medium B. bubo 624 Mountaineering, rock climbing, speleology medium A. chrysaetos, G. fulvus 600 Sport and leisure structures low A. chrysaetos, B. bubo Figure 6: Characteristic landscape of the IBA Šar Planina Mountain (photo: Lj. Melovski) Slika 6: Zna~ilna krajina IBA Šar planina (foto: Lj. Melovski) pairs) and Eagle Owl (5—10 pairs) in the country, but the main reason for its designation is the presence of the country's largest populations of four species characteristic of the Eurasian high-montane biome. One pair of Lammergeier Gypaetus barbatus had also bred there until 1981 (Grubač 1990). Historical breeding records of Capercaillie Tetrao urogallus also exist (Matvejev 1957), but it has not been confirmed since that period, although good habitats offer possibilities for its survival and, furthermore, the species was registered on the northern slopes of the mountain (Puzovic et al. 2009). Until 1990s, non-breeding Griffon Vultures had also been frequent (Grubač 1997), but their number have significantly decreased in the last several years. Other species that are limited to the alpine biome in the Balkan Peninsula and have important national populations on Šar Planina Mt are the Red-billed Chough (50—100 pairs in 1980s, B. Grubač unpubl., but have probably declined since then) and Shore Lark (Table 8). Habitats and land use Large parts of the site are situated above 1,600 m altitude, dominated by pastures on silicate and calcareous bedrocks, as well as heathland with bilberry Vaccinium spp. and Common Juniper Juniperus communis. Both silicate and calcareous cliffs are present, especially in the central part of the mountain (the complex Lešnica in the Pena River Valley). Moorlands are also found around the spring areas of almost all larger rivers (Table 9). Broad-lived forests are dominated by Beech Fagus sylvatica, on some places mixed with Bulgarian Fir Abies borisii-regis. Conifer forests are dominated by the latter, although Spruce Picea abies and Molika Pine Pinus peuce are also present. Around the villages, the natural vegetation is strongly modified. Principal activities are livestock breeding and forestry (Figure 6). Threats Poaching of all game species, possibly including birds of prey, regularly takes place. The area has been in the centre of the armed conflict from 2001, and it is estimated that large numbers of illegally held weapons are present in the region, resulting in widespread poaching, most likely including important bird species and their prey base. Both commercial and illegal logging takes place. Reduction of livestock numbers, especially sheep, has likely influenced the population of the Choughs and vultures. The mountain is a popular mountaineering destination. Construction of new roads and hotels is also planned (Table 10). Conservation The westernmost part of the site falls within the boundaries of Mavrovo National Park. A small protected area (Popova Šapka) lies in the central part of the mountain. Establishment of a new national park, "Šar Planina Mt", is planned, which will entirely cover the rest of the site. The region is also an Emerald Site (MK0000008). 3.2.2. Radika River Catchment Name in English: Radika River Catchment Name in Macedonian: Sliv na reka Radika (CHHB Ha peKa PaguKa) IBA code: MK002 Criteria: A3, B2 Area: 70,392 ha Central coordinates: 20o39'53.95"E, 4lo40'47.09"N Altitude: 610-2,764 m a.s.l. Administrative region(s): Gostivar, Rostuše-Mavrovo, Debar, Drugovo, Zajas Site description The site adjoins Šar Planina Mt (MK001) to the SW, while its western boundary follows the national border with Albania in NW Macedonia. The boundary to the south passes under the village of Skudrinje, follows the Mala Reka and Garska Reka Rivers to the locality known as Jama, where it turns north, following the ridges of Dumovica (2,023 m a.s.l.), Pašinica (1,890 m a.s.l.), Ahmetovica (1,901 m a.s.l.), Mali Šar (l,993 m a.s.l.), Aramiski Kamen (1,700 m a.s.l.), Dejanovec (1,622 m a.s.l.) and Vlainica (1,304 m a.s.l.), from where it turns west and, after passing Bunec, reaches Mala Planina. It occupies small parts of Šar Planina Mt, almost entire Mt Korab and a significant part of Mt Bistra, including Mavrovo Reservoir. The site General information Table 11: List of triggering and other important bird species in the IBA Radika River Catchment Tabela 11: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Povodje reke Radike Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Prunella collaris B 2002 10-50 C A3 Tichodroma muraria B 2002 10-20 C A3 Pyrrhocorax graculus B 2005 100-200 C A3 Montifringilla nivalis B 1998 10-30 C A3 Aquila chrysaetos R 2008 4-6 B B2 Crex crex B 2010 30-100 C B2 Bubo bubo R 2008 8-15 C B2 Monticola saxatilis B 2002-2010 30-100 C B2 Falco tinnunculus R Common B2? Gyps fulvus N 2006 5-10 ind. C N Eremophila alpestris balcanica B Common N Pyrrhocorax pyrrhocorax B Frequent N Table 12: The main CORINE land cover types (Level 3) in the IBA Radika River Catchment Tabela 12: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Povodje reke Radike Code/ Koda CORINE land cover type/ tip pokrovnosti in rabe tal Coverage/ Pokrovnost (%) 311 Broad-leaved forest 42.0 321 Natural grasslands 34.5 322 Moors and heathland 5.1 324 Transitional woodland-shrub 8.7 Other 9.7 was formerly named "Korab Mt and Radika Gorge" (Heath & Evans 2000). Only minor corrections to the former site's boundaries have been made, in order to follow the natural features and/or boundaries of Mavrovo National Park. The site characterizes a complex relief structure, with high mountains, deep river valleys and gorges. The highest mountain in Macedonia — Korab — is located here (summit Golem Korab 2,764 m a.s.l.). The geological composition is diverse, with formations from different periods. Also characteristic is the limestone on Mt Bistra. The site's main water bodies are the Radika River and Mavrovo reservoir (Figure 7). almost identical bird community composition and ornithological importance. The list of registered bird species amounts to over 140 species (Velevski et al. 2003A, Micevski 2010). Triggering species are the Golden Eagle (4-6 pairs) and Eagle Owl (8-15 pairs), but populations of the four species characteristic of the Eurasian high-montane biome, occurring mostly in the highest parts of Mt Korab above 2,200 m a.s.l. are also relatively large. The site holds internationally important populations of Rock Partridge and Rock Thrush, while Common Kestrel, Red-billed Chough and Shore Lark are probably also present with important populations. Non-breeding Griffon Vultures used to have important roosting site here, numbering up to 60 individuals in the 1990s (Grubač 1997), but are now seen only sporadically (Table 11). The Black Vulture Aegypius monachus and Lammergeier Gypaetus barbatus have also been known to occur here (Grubač 1998 & 2002). Habitats and land use Broad-leaved forests are dominated by oaks (several species and communities) and Beech Fagus sylvatica. Very often, mixed Beech and Bulgarian Fir Abies borisii-regis forests are found, as well as mixed oak and fir forests in some places. Fir forests form pure stands. A smaller pure stand of Spruce Picea abies is also present. High-montane grasslands used as summer pastures for livestock and heathlands are the second dominant habitat type here (Table 12), but general landscape is formed by steep limestone cliffs (Figure 8). Threats Although protected as a national park, poaching is common in the border regions, and prob ably had direct and indirect impacts on raptors (direct persecution, Table 13: The main threats to birds and their importance in the IBA Radika River Catchment Tabela 13: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Povodje reke Radike Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 960 Interspecific faunal relations high A. chrysaetos, B. bubo, G. fulvus 141 Abandonment of pastoral systems medium P. graculus, G. fulvus 160 General forestry management medium forest species 243 Trapping, poisoning, poaching medium G. fulvus, A. chrysaetos 410 Industrial or commercial areas medium A. chrysaetos, P. graculus, P. collaris, M. nivalis 501 Paths, tracks, cycling tracks low A. chrysaetos 624 Mountaineering, rock climbing, speleology low A. chrysaetos, G. fulvus 530 Improved access to site low A. chrysaetos, G. fulvus Figure 7: Map of the IBA Radika River Catchment with its main features depicted Slika 7: Zemljevid IBA Povodje reke Radike z glavnimi zna~ilnostmi obmo~ja Species Biogeographically and ecologically, the site is almost identical to Šar Planina Mt, thus boasting Figure 8: Characteristic landscape of the IBA Radika River Catchment (photo: Lj. Melovski) Slika 8: Zna~ilna krajina IBA Povodje reke Radike (foto: Lj. Melovski) prey base reduction, disturbance). Some 9,000 inhabitants live in the region, partially depending on its natural resources, especially pastures and forests. Decrease in the number of livestock, especially sheep, has been significant, probably having a negative impact on vulture populations and Choughs. The National Park management implements forest management practices that should be improved to maintain higher biodiversity. Construction of two hydro-power plants with reservoirs and connected water-supply channels meant to provide water from streams as much as 18 km far is planned for near future. One of them, "Boškov Most", is located on the site's southern boundary, while the other, "Lukovo Pole", is in the core area, which no doubt means that significant deterioration can be expected. In addition, at least six small hydro-power plants are planned, some of them in highly sensitive regions (Table 13). Conservation The entire site lies within the boundaries of Mavrovo National Park, which has been also identified as an Emerald Site (MK0000007). The first management plan of the Park is presently under development by the Park's management and Oxfam Italia (2009-2010). Two very small protected areas (Dlabok Dol and Garska Reka) are also located within this site. 3.2.3. Lake Ohrid General information Name in English: Lake Ohrid Name in Macedonian: Ohridsko Ezero (OxpugcKo E3epo) IBA code: MK005 Criteria: A4iii, B1i, B2 Area: 24,736 ha Central coordinates: 20o43'52.65"E, 41o03'36.88"N Altitude: 695-900 m a.s.l. Administrative region(s): Struga, Debarca, Ohrid Site description Situated in the SW of the country, this site includes part of Lake Ohrid, following its shore line and the national border with Albania, which runs across the lake surface. The site is adjacent to the Albanian IBA site "Lake Ohrid" (AL002, Heath & Evans 2000). The shore line of the lake is polygenetic, with limnogene shore (from lake sediments) situated in the north. At Ljubaništa and St. Naum there is the potamogene coast, while the western slopes of Mt Galičica are of tectogene and abrasive origin, with characteristic cliffs. The coastline is dominated by Triassic limestones. The lake is tectonic, some 3 million years old, with max. depth of 286 m (Figure 9). Species The site's bird fauna has been studied relatively well (Micevski 2003), although precise quantitative data and estimates for the breeding species are missing. In total, 89 waterbird species have been recorded, including the arable land and swamps surrounding the lake (presently largely dried and of little importance). Winter census data are available for the periods 1987-1991, 1997-2000, 2002, 2010 and 2011 (Micevski 1996, Micevski 1998, Fremuth et al. 2000, Wetlands International in litt., MES unpubl.). The total number of wintering waterbirds on the lake surface (Macedonian part only) was between 79,000 individuals in 1989 (Wetlands International in litt.) and 24,000 individuals in 1997 (Fremuth et al. 2000), but only about 10,000 and 17,000 were counted in 2010 and 2011, respectively (MES unpubl.). The most numerous species is the Coot (as many as 60,000 ind. in 1989, but only 7,500 in 2010), followed by the Pochard (500-7,000 ind., but only 150 and 300 in 2010 and 2011, respectively), Red-crested Pochard (350-7,000 ind.), Tufted Duck (240-6,500 ind., but only 20 in 2010) and Black-necked Grebe (130-3,600 ind.). There was a substantial decrease in numbers of the latter in the period after 1991, and the threshold of 2,200 individuals has not been met again after then. Triggering species for the breeding period are the Pygmy Cormorant with some 50-100 pairs breeding in 2000 (Micevski 2003), which has met also the B1i criteria only in 1989 and 2002 (Micevski 1996, Wetlands International in litt.), and the Goosander, which most probably bred there in 2006 (Skorpi'kova et al. 2006). The Great Crested Grebe is Figure 9: Map of the IBA Lake Ohrid with its main features depicted Slika 9: Zemljevid IBA Ohridsko jezero z glavnimi zna~ilnostmi obmo~ja Table 14: List of triggering and other important bird species in the IBA Lake Ohrid Tabela 14: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Ohridsko jezero Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji all watetbitds W 1987- 2002 20,000-79,000 ind. A A4iii Podiceps nigricollis W 1988 1991 2,600-3,600 ind. A B1i Netta rufina W 1987- -2011 350-7,000 ind. A B1i Fulica atra W 1987- -2011 13,000-60,000 ind. A B1i Mergus merganser B 2006 1-3 A B1i Phalacrocorax pygmeus B 2000 50-100 C B2 Podiceps cristatus W 1991- 2000 800-1,400 ind. A N Podiceps cristatus B -2003 20-100 C N Phalacrocorax pygmeus W 1989- 2002 1,100-3,250 ind. A N Aythya ferina W 1987- 2000 500-7,000 ind. A N Aythya fuligula W 1989- -1999 240-6,500 ind. A N Figure 10: Characteristic landscape of the IBA Lake Ohrid (photo: S. Hristovski) Slika 10: Zna~ilna pokrajina IBA Ohridsko jezero (foto: S. Hristovski) Table 15: The main CORINE land cover types (Level 3) in the IBA Lake Ohrid Tabela 15: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Ohridsko jezero Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 512 Water bodies 99.6 Other 0.4 considered one of the most frequent breeding birds on the Lake (Micevski 2003) (Table 14). The northern shallow part of the lake is of the highest importance for wintering waterbirds (Micevski 1996), with the Coot and Red-crested Pochard being the most abundant, which is explained by the presence of extensive reedbeds, underwater Chara vegetation and influx of nutrients by the Satoka River. Habitats and land use The lake constitutes the greater part of the site (Table 15). Cliffs along the western and especially eastern shoreline are also part of the site. The most extensive reedbeds are found on the northern shore of the Lake, although small reed patches can be found along the entire shoreline. The lake is oligotrophic. Smaller xerophylous oak forests are found within the site boundaries (Figure 10). Threats Lake Ohrid is an attractive tourist destination, and practically the entire shoreline is strewn with tourist Table 16: The main threats to birds and their importance in the IBA Lake Ohrid Tabela 16: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Ohridsko jezero Code/ Koda Threat/ Dejavnik ogrožanja Threat impact/ Vpliv Most affected species/ Najbolj prizadete vrste 600 803 Sport and leisure structures Infilling of ditches, dykes, ponds, marshes or pits high high M. merganser P. pygmeus resorts. For the needs of tourism, beeches are expanded and reedbeds removed or dried out. Eutrophication probably takes place (Table 16). No zoning concept has been implemented. Conservation The Lake is protected as a Nature Monument, and is also proposed as an Emerald Site (MK0000024). Together with the town of Ohrid and its wider surrounding, it is listed on UNESCO's list of World Natural and Cultural Heritage Sites. The site also includes a small portion of Galičica National Park. 3.2.4. Lake Prespa General information Name in English: Lake Prespa Name in Macedonian: Prespansko Ezero (npecnaHCKO E3epo) IBA code: MK006 Criteria: A1, A4i, B1i, B2 Area: 19,842 ha Central coordinates: 21o00'43.56"E, 40o55'58.94"N Altitude: 850-970 m a.s.l. Administrative region(s): Resen Site description The site includes the Macedonian part of Lake Prespa (Macro Prespa) in SW Macedonia, cliffs on its shoreline and swamps near the villages of Stenje and Nakolec, as well as wet meadows, reedbeds and fishponds between the villages of Sir Han and Asamati. It is adjacent to the sites "Lake Megali Prespa" (AL003) in Albania and "Lake Mikri Prespa and Lake Megali Prespa" (GR047) in Greece (Heath and Evans 2000). Lake Prespa's coast is polygenetic; the east coast (slopes of Mt Pelister) is of potamogene character as a result of several river inflows from the mountain (Brajčinska Reka, Kranska Reka etc.). The northern coast is basically of limnogene character, and along the northern shoreline it is of phytogene origin (owing to its wetland vegetation). On the western coast, the shoreline is of abrasive character, with notable cliffs, as a result of the geological composition represented by Triassic limestone. The most important river is the Golema Reka in the north. The max. depth of the lake reaches 54 m (Figure 11). Species Bird fauna of Lake Prespa is among the best studied in the country (Micevski 1998). In total, 103 waterbird species have been recorded. Winter censuses data are Figure 11: Map of the IBA Lake Prespa with its main features depicted Slika 11: Zemljevid IBA Prespansko jezero z glavnimi zna~ilnostmi obmo~ja available for the periods/years 1987-1990, 19972002, 2004-2006 and 2009-2011 (Micevski & Schneider 1997, Fremuth et al. 2000, Vasic 2009A, Wetlands International in litt., MES unpubl.). The most numerous has been the Coot (1,000-20,700 ind.), followed by Tufted Duck (between as few as 12 ind. in 2002 and 9,000-12500 ind. in 19881989), Black-necked Grebe (up to 5,800 in 2004, with decline in numbers thereupon, the exception being 2009 with 3900 ind.), Pochard (12,500 ind. in 1988, 9,000 ind. in 1989, but only 15 ind. in 2004), and Teal Anas crecca (up to 2,500 ind.). The total number of wintering waterbirds exceeded 20,000 individuals only in 2009, when 31,500 waterbirds were counted (Vasic 2009A). The island Golem Grad holds the largest Cormorant colony in the country (2,500-3,000 pairs, VAsic 2010) and the only colony (ca. 50 pairs) of the Yellow-legged Gull in Macedonia (VAsic 2009A). 30-50 pairs of Goosander breed along the lake shores (VAsic 2010), with some of them also wintering on the lake. Up to Table 17: List of triggering and other important bird species in the IBA Lake Prespa Tabela 17: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Prespansko jezero Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Pelecanus crispus N 2008- -2010 300-1,000 ind. C A1, A4i, B1i Pelecanus onocrotalus N 2008- -2010 150-500 ind. C A4i, B1i Mergus merganser B 2008- -2010 30-50 B B1i Mergus merganser W 1987- -2011 2-22 ind. A B1i Ixobrychus minutus B 2009 50-200 C B2 Podiceps cristatus W 2010- -2011 2,000-3,400 ind. A N Podiceps cristatus B 1987- 2010 100-600 C N Podiceps nigricollis W 1989- 2004 1,400-5,800 ind. A N Phalacrocorax pygmeus B 1993 10-20 C N Phalacrocorax carbo sinensis B 2008 -2010 2,500-3,000 B N Casmerodius albus N 2010 60-150 ind. B N Anas strepera B -1998 0-10 C N Aythya nyroca B 1998- 2008 3-10 B N Aythya ferina W 1989- 1999 1,850-3,200 ind. A N Aythya fuligula W 1988- -1997 100-9,000 ind. A N Fulica atra W 1997- -1998 9,000-9,750 ind. A N 300 individuals of Dalmatian Pelican and up to 100 individuals of White Pelican can be seen concurrently on the lake surface. Both pelican species breed at Lake Mikri Prespa in Greece with estimated 1,169 pairs of Dalmatian and 332 pairs of White Pelican in 2010 (Society for Protection of Prespa 2011). They visit Lake Macro Prespa for feeding (when they can be readily seen accompanying fishermen's boats) and roosting, especially along the shoreline between the villages of Konjsko and Stenje. On the basis of these numbers, we have estimated the number of non-breeding birds present in the Macedonian part of Lake Prespa at 300-1,000 individuals of the Dalmatian Pelican and 150-500 individuals of the White Pelican. The population of the Ferruginous Table 18: The main CORINE land cover types (Level 3) in the IBA Lake Prespa Tabela 18: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v IBA Prespansko jezero Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 512 Water bodies 91.0 411 Inland marshes 4.9 Other 4.1 Duck has been estimated at only 3-4 pairs breeding in the presently dry fishpond at Asamati village in 1995 (Micevski 1998), and at 3-10 pairs by VAsic (2010). The probable breeding population of the Gadwall has also been estimated to 10 pairs at the most (Vasic 2010), supposedly on the grounds of observations by Micevski (1998) in the breeding period. Some 20-50 breeding pairs of the Great Egret have been estimated to breed at Lake Prespa (Vasic 2010), although the breeding colony may possibly resides in its entirety in Greece. Still, the species uses the Macedonian part of the lake for foraging as well. Micevski (1998) reports on minimum 30 breeding pairs of the Great Crested Grebe along the northern shore, while Vasic (2010) gives an estimate at 500750 pairs for Galičica National Park (both Ohrid and Prespa shorelines included), which gives a rather imprecise, but still high estimate of the breeding population at 100-600 pairs (Table 17). Habitats and land use The lake surface constitutes the greater part of the site, but extensive reedbeds are found along the northern shore (between the villages of Sir Han and Asamati), and along the eastern shoreline (near Stenje and at Nakolec) (Table 18). Remains of riparian forests can also be seen. There are two drained fishponds with recent plans for reactivation. Large sand beach in process of succession is found around the village Figure 12: Characteristic landscape of the IBA Lake Prespa (photo: Lj. Melovski) Slika 12: Zna~ilna krajina IBA Prespansko jezero (foto: Lj. Melovski) of Stenje on the northern shore. Wet meadows and Carex fields spread around the village of Perovo. Cliffs are present on the island Golem Grad and between Stenje and Konjsko villages, overgrown by old Greek Juniper Juniperus excelsa forests (Figure 12). Threats Sand extraction and conversion of meadows into intensively managed orchards are widely practiced by the local population. Poaching is also common. Tourism activities have decreased in the last two decades, although plans for the construction of new hotels exist. Water quality decreased, and the lake is presently treated as eutrophic (Levkov et al. 2007) (Table 19). Conservation The entire lake is protected as a Nature Monument; since 1996, its northern shallow parts and shores have been protected as Strict Nature Reserve Ezerani Table 19: The main threats to birds and their importance in the IBA Lake Prespa Tabela 19: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Prespansko jezero Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 100 Cultivation high I. minutus 701 Water pollution high wintering waterbirds 952 Eutrophication high wintering waterbirds 243 Trapping, poisoning, poaching medium Anatidae 600 Sport and leisure structures medium P. crispus, P. onocrotalus 803 Infilling of ditches, dykes, ponds, marshes or pits medium A. nyroca, I. minutus (2,080 ha). This reserve is presently in the process of re-proclamation (in the category Nature Park), and new boundaries covering 1,917 ha are propose. Temporal and spatial zoning of the lake surface in order to preserve waterbirds is missing. The coast from Sir Han to the border with Albania and the island Golem Grad are integrated into Galičica National Park. All three protected areas are proposed as Emerald Sites (MK0000001, MK0000002 and MK0000025, respectively). It is also a Ramsar Site of international importance, among other criteria due to its importance for waterbirds. Management plans are under development for Galičica and Ezerani. Name in English: Demir Kapija Gorge Name in Macedonian: Demirkapiska Klisura (^eMHpKanHCKa Knncypa) IBA code: MK008 Criteria: A1, A3, B2 Area: 9,665 ha Central coordinates: 22o18'20.44"E, 41o23'46.84"N Altitude: 110-928 m a.s.l. Administrative region(s): Demir Kapija, Gevgelija, Konče, Valandovo Site description Situated E-SE of the town of Demir Kapija in southern Macedonia, the site includes about a half (upper part) of the longest gorge of the Vardar River (in total ca. 20 km long). The border runs along the last houses of Demir Kapija, turns south towards Čiflik and Dren villages, then follows the Drenska Reka (a tributary of the Vardar) to the east to the Stefan ridge, where it turns north. Then it continues towards the hills of Študer (609 m a.s.l.) and Veternikot, crosses the Vardar and, by following the ridges of Ilovski Čukar (524 m a.s.l.), Golem (928 m a.s.l.) and Mal Karadag (707 m a.s.l.), reaches Vaganar (880 m a.s.l.). From there it turns west and follows the intermittent rivulets Linan Dere and Dobroište, runs through Iberlija village and follows the Lesovo rivulet to Kurtlu Čuka. Then it continues south, and via Sreden Rid (556 m a.s.l.) descends to the Vardar River, crossing it at Demir Kapija. In this way, the border is strongly modified as for the one in Heath & Evans (2000). Main morphological characteristic is the gorge, which is in certain parts a typical canyon with walls of over 200 m high. Jurassic limestones are dominant in the beginning of the gorge, while in the SE the geological composition is of Jurassic magmatic rocks. Main tributaries of the Vardar are the Iberliska (Čelevečka) Reka (forming a typical canyon) and the Golema Javorica (Figure 13). 3.2.5. Demir Kapija Gorge General information Table 20: List of triggering and other important bird species in the IBA Demir Kapija Gorge Tabela 20: Seznam kvalifikacijskih in drugih pomembnih vrst v IBA Soteska Demir Kapija Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2006-2010 2-3 A A1 Alectoris graeca R Common A3 Oenanthe hispanica B Common A3 Sylvia cantillans B Abundant A3 Sitta neumayer R Common A3 Emberiza melanocephala B Frequent A3 Circaetus gallicus B 2007 5-8 B B2 Accipiter brevipes B 2005 4-6 B B2 Ciconia nigra B 2010 1 A N Gyps fulvus R 2009-2010 6-7 A N Buteo rufinus R 2010 1-2 B N Milvus migrans B 2010 1 A N Aquila pennata B 2010 1 A N Aquila chrysaetos R 2010 1-2 A N Falco biarmicus B 2007 0-1 B Falco peregrinus R 2009 2 B N Bubo bubo R 2005 3-5 B N —i---1-1-1-1-r— 22'12'e 22'15'e 22*1 be 22'21'E Figure 13: Map of the IBA Demir Kapija Gorge with its main features depicted Slika 13: Zemljevid IBA Soteska Demir Kapija z glavnimi zna~ilnostmi obmo~ja Species This location is best known by the birds of prey breeding on limestone cliffs, especially Griffon and Egyptian Vultures. Both had undergone strong decline; in 1996, their breeding populations were estimated at 16 and 10 pairs (Grubač 1997 & unpubl.), but numbered only six and two pairs in 2010, respectively. The Griffon Vulture colony there is one of the only three remaining breeding colonies in Macedonia. The total number of all registered bird species reached 149 (Rolevski et al. 2003). Today, the site is one of the five most important localities in the country for the Short-toed Eagle (5-8 pairs), whose breeding density with 0.5 pairs/10 km2 is the highest in the country (Velevski & Grubač 2008). Riparian Oriental Plane forests are very favourable for the breeding of the Levant Sparrowhawk (4-6 pairs). Among other species rarely found in Macedonia are the Booted Eagle, Black Kite, Black Stork, Long-legged Buzzard, etc. Most abundant among the Table 21: The main CORINE land cover types (Level 3) in the IBA Demir Kapija Gorge Tabela 21: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v IBA Soteska Demir Kapija Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 242 Complex cultivation patterns 5-7 311 Broad-leaved forest 21.6 332 Bare rocks 0-3 323 Sclerophyllous vegetation 34-8 324 Transitional woodland-shrub 33-2 Other 4-4 species characteristic of the Mediterranean biome is the Subalpine Warbler (presumably one of the highest densities in the country) in the pseudomaquis, and the Rock Nuthatch on the limestone cliffs (Table 20). Figure 14: Characteristic landscape of the IBA Demir Kapija Gorge (photo: M. Velevski) Slika 14: Zna~ilna krajina IBA Soteska Demir Kapija (foto: M. Velevski) Table 22: The main threats to birds and their importance in the IBA Demir Kapija Gorge Tabela 22: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Soteska Demir Kapija Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 243 Trapping, poisoning, poaching high G. fulvus, N. percnopterus, A. chrysaetos, A. graeca 141 Abandonment of pastoral systems high G. fulvus, N. percnopterus 230 Hunting high G. fulvus, A. graeca 160 General forestry management medium C. nigra, A. pennata, M. migrans, C. gallicus 502 Motorways, roads medium G. fulvus, N. percnopterus, C. gallicus, A. brevipes 624 Mountaineering, rock climbing, speleology medium G. fulvus 301 Quarries medium C. gallicus, Mediterranean bird assemblage 410 Industrial or commercial areas medium G. fulvus, N. percnopterus, A. chrysaetos, C. gallicus, A. pennata 730 Military manoeuvres medium G. fulvus 400 Urbanised areas, human habitation low G. fulvus, A. chrysaetos, A. graeca Habitats and land use Limestone cliffs dominate the landscape, but degraded pseudomaquis with dominance of Kermes Oak Quercus coccifera is the prevailing forest community. At some locations, mature oak forests with significant presence of Silver Lime Tilia argentea are found, while along the Vardar and all smaller rivers, Oriental Plane Platanus orientalis belts are present (Table 21, Figure 14). Threats Hunting and poaching regularly take place, and use of poisonous baits was common until recently. Cliffs attract cliff-climbers, but are also used for military training. Depopulation of the villages resulted in a drastic decrease in livestock numbers, reducing food source for vultures. Illegal wood extraction for heating and construction purposes takes place along with official forest management practices. The reconstruction of E-75 highway from Skopje to Thessaloniki (Greece) is another serious threat the site will face in the near future. High disturbance is expected during the reconstruction phase, and somewhat less during the operation phase. Also, a plan for wind farm construction in the area has been prepared (Table 22). Conservation Part of the site is protected as a Nature Monument, but the protected site does not include some of the key localities. Also, parts of the valley of the Iberliska Reka River are under protection. It is proposed as an Emerald Site (MK0000005), but boundaries of this site have not been suitably defined as yet. 3.2.6. Lake Dojran IBA code: MK010 Criteria: A1, A4i, B1i, B2 Area: 2,691 ha Central coordinates: 22o44'3. 00"E, 4lo12'51.81"N Altitude: 150 m a.s.l. Administrative region(s): Nov Dojran Site description The site is located in the SE part of the country, and includes the Macedonian part of Lake Dojran, together with the surrounding wetland vegetation. It adjoins the site "Lake Doirani" (GR023) in Greece (Heath & Evans 2000). The coast is limnogene, consisting of the lake sediments. It is a shallow tectonic lake with maximum depth of 10 m (Figure 15). Species The avifauna has been insufficiently studied; the complete list numbers only 84 waterbird species (Micevski 2000, Micevski 2002/2003, Velevski & Saveljic 2010, Hanžel 2010). However, for 12 species only single records are at hand. Data from winter censuses are available for the periods/years: 1982-1983, 1985, 1987-1990, 2002, and 20102011 (Micevski 1991, Wetlands International in litt., MES unpubl.). The total number of wintering waterbirds ranges from only 700 individuals in 2002, 3,200 in 2010, and up to 19,000 individuals in 1989. Most abundant are the Coot (between only 81 ind. in 2002 and 10,000 ind. in 1989), Pochard (up to 5,600 in 1990) and Tufted Duck (up to 3,000 in 1989). Of highest importance is the winter presence of Dalmatian Pelicans (330 ind. in 2002 and 450 in 2010) and Pygmy Cormorants (230 ind. in 1990). Other important species include 2-5 breeding pairs of Ferruginous Duck (Micevski 2000), Bittern (at least two pairs, Skorpi'kova et al. 2006) and Little Bittern, whose breeding population has been estimated at a minimum of 30 pairs (Micevski 2000). A flock of min. 70 White Pelicans has been observed in spring 2010 (J. Hanželpers. comm.). A single record of Red-breasted Goose Branta ruficollis exists (12 ind. on 14 General information Name in English: Lake Dojran Name in Macedonian: Dojransko Ezero (^ojpaHCKO E3epo) Table 23: List of triggering and other important bird species in the IBA Lake Dojran Tabela 23: Seznam kvalifikacijskih in drugih pomembnih ptic v IBA Dojransko jezero Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Pelecanus crispus W 2OO2-2O1O 300-450 ind. A A1, A4i, B1i, B2 Ixobrychus minutus B 2OOO 30-60 B B2 Botaurus stellaris B 2006 2-6 B B2? Pelecanus onocrotalus N 2010 70 ind. A N Phalacrocorax pygmeus W 1988-2011 20-230 ind. A N Aythya nyroca B 2000 2-5 C N Aythya fuligula W 1987-1990 200-3,000 ind. A N Fulica atra W 1989-2011 800-10,000 ind. A N Aythya ferina W 1988-2002 220-5600 ind. A N Ü 0 5 1 2 3 4 km NOV DOJRAN \ N' T t. t k t D t> i r 9 n GR Dat> \ I SS Trn 1 STAR DOJRAN ^-I J J SRETENOVO J V A ) V SvSpsfro Brfo \ 361 m / '4ce «' l ;; .u'+jt j l .'.(j t a j/l Figure 15: Map of the IBA Lake Dojran with the main features depicted Slika 15: Zemljevid IBA Dojransko jezero z glavnimi zna~ilnostmi obmo~ja Feb 2003, E. Stoynov & Y. Iliev unpubl.), being only the second for the whole country (Table 23). Habitats and land use The lake surface constitutes the greater part of the IBA, with reedbeds along most of its shore included (Table 24). After withdrawal of the water during drying-up Table 24: The main CORINE land cover types (Level 3) in the IBA Lake Dojran Tabela 24: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v IBA Dojransko jezero Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 512 Water bodies 86.0 411 Inland marshes 9.7 Other 4.4 of the lake in the past, muddy shores were used for agriculture. The lake is eutrophic (Figure 16). Threats The lake was seriously threatened by drying out in the 1995-2002 period due to droughts and excessive water exploitation. Hydrological conditions have improved since, and supplementary water inflow has been secured, resulting in return of the water to the previous level. Intensive fishing, in which birds were formerly used, continues almost permanently (Apostolski & Matvejev 1955). In the summer period, the lake is a popular tourist destination. A wind farm has been constructed on the Greek side of the Lake basin, probably impacting Dalmatian Pelicans and other waterbirds (Table 25). Conservation The lake is protected as a Nature Monument. It is a Ramsar Site of international importance owing to its significance for waterbird populations, and an Emerald Site (MK0000003). Apart from ensuring additional water inflow into the Lake, no other conservation activities are taking place here. Table 25: The main threats to birds and their importance in the IBA Lake Dojran Tabela 25: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Dojransko jezero Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 410 Industrial or commercial areas high P. crispus 210 Professional fishing high P. crispus, A. nyroca 600 Sport and leisure structures high B. stellaris 3.2.7. Zletovska River Valley Name in English: Zletovska River Valley Name in Macedonian: Dolina na Zletovska Reka (öp^HHa Ha 3^eT0BCKa PeKa) IBA code: MK012 Criteria: A1, B2 Area: 12,687 ha Central coordinates: 22o10'25.28"E, 41o55'52.66"N Altitude: 310—867 m a.s.l. Administrative region(s): Probištip, Češinovo - Obleševo, Kočani, Sveti Nikole Site description The site occupies the valley of the Zletovska Reka River south of the villages of Pišica and Novoselani, the SW slopes of Mt Osogovo and the eastern slopes of Mt Mangovica in NE Macedonia. Its SW boundary follows the ridge of Mangovica north of the village of Gorno Barbarevo, then continues SE to Petrišino village, passes the river valley at Globica village and proceeds east below the villages of Buneš and Rajčani, following the ridge formed by the peaks of Blatec (825 m a.s.l.), Božurnjak (767 m a.s.l.) and Uši (628 m a.s.l.), and descending SW to the village of Sokolarci. From there, it follows the irrigation channel General information Table 26: List of triggering and other important bird species in the IBA Zletovska River Valley Tabela 26: Seznam kvalifikacijskih in drugih pomembnih vrst v IBA Dolina Zletovske reke Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Aquila heliaca R 2009 3-4 A A1, B2 Burhinus oedicnemus B 2008 5-20 C N Circus pygargus B 2008 3-10 C N Falco cherrug B 2003 0-1 A N Coracias garrulus B 2008 1-5 C N Figure 17: Map of the IBA River Zletovska valley with its main features depicted Slika 17: Zemljevid IBA Dolina Zletovske reke z glavnimi zna~ilnostmi obmo~ja westwards to the village of Novoselani. The boundary has been largely modified from the original proposal by E. Stoynov from 2003 and excludes the rice fields along the Bregalnica River. The site is characterized by low, undulating hilly and mountainous relief with dominant valley of the Zletovska Reka River and several intermittent streams in the western parts of the site. The geological composition is diverse, with magmatic rocks of Kratovo - Zletovo volcanic region and different metamorphic and alluvial sediments along the river (Figure 17). Species No detailed species list for the site is available, although ca. 80 species have been registered so far. Most important are the Imperial Eagle (3-4 pairs) and Stone Curlew (5-20 pairs), breeding on the hilly slopes with dry pastures and in remains of oak forests (Imperial Eagle), although the Roller (up to five breeding pairs) and a possible breeding of the Saker Falcon (one pair) have also been recorded. Up to 10 pairs of Montagu's Harrier also breed here (Table 26). Table 27: The main CORINE land cover types (Level 3) in the IBA Zletovska River Valley Tabela 27: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v IBA Dolina reke Zletovske Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 211 Non-irrigated arable land 34.0 242 Complex cultivation patterns 18.0 243 Land principally occupied by 10.9 agriculture, with significant areas of natural vegetation 231 Pastures 15.3 324 Transitional woodland-shrub 17.8 Other 3.9 Figure 18: Characteristic landscape of the IBA Zletovska River Valley (photo: M. Velevski) Slika 18: Zna~ilna krajina v IBA Dolina Zletovske reke (foto: M. Velevski) Table 28: The main threats to birds and their importance in the IBA Zletovska River Valley Tabela 28: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Dolina Zletovske reke Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 141 Abandonment of pastoral systems high B. oedicnemus 243 Trapping, poisoning, poaching high A. heliaca 101 Modification of cultivation practices medium C. ciconia 410 Industrial or commercial areas medium A. heliaca Habitats and land use The greater part of the lowland is used for agriculture, while the surrounding hills are typical dry pastures with remains of xerophylous oak forests, somewhat better preserved in the ravines. Poplar and willow belts have developed along the river (Table 27, Figure 18). Threats Threats are not well documented, but very likely include reduction of livestock numbers and poaching. Wind farm planned north of Sveti Nikole is also likely to affect Imperial Eagles breeding at this site. Conservation The site is not protected. 3.2.8. Tikveš Region General information Name in English: Tikveš Region Name in Macedonian: Tikveški region (THKBemKH peruoH) IBA code: MK013 Criteria: A1, B2 Area: 18,696 ha Central coordinates: 22o08'1.46"E, 41o25'6.82"N Altitude: 160-855 m a.s.l. Administrative region(s): Negotino, Demir Kapija, Kavadarci Site description Site is situated in the southern-central parts of Macedonia, south of the town Negotino. The boundary starts at Pepelište village, crosses the Vardar, continues south to the village of Dolni Disan, then SW to the village of Moklište, continues along the road on the Vitačevo plateau to the crossroad towards the village of Stragovo, descends to this village, continues NE above the villages of Vešje and Besvica to the E-75 Skopje—Gevgelija highway, follows it east almost to Demir Kapija, crosses the Vardar and turns north to Korešnica village, then north to Široki Kuk, NW to the village of Brusnik and west back to the village of Pepelište (Figure 19). The site is dominated by hills formed as a result of erosion that has shaped the bottom sediments of the Pliocene lake. The Vitačevo Plateau in the SW is composed of volcanogenic tuffs. Species The site classifies on the basis of two Egyptian Vulture pairs in its southern part and some 230-250 breeding pairs of Lesser Kestrel in the northern part, breeding exclusively in the villages. Northern part also includes the Vardar River Valley, where 1-2 pairs of Imperial Eagles breed. At least one pair of Lanner Falcon has been found, although there are indications that a second pair inhabits the area as well. Within this site, the dump site Dubrovo is situated, which formerly (1980-1991 period) attracted up to 120 individuals of Egyptian Vultures prior to their migration (B. Grubač unpubl), as well as a fishpond at the village of Bistrenci that presumably used to attract large numbers of migratory waterbirds. This fishpond has been dried out and converted into arable land; unfortunately, no systematic surveys of the bird fauna have ever been carried out there. The site also holds the largest Table 29: List of triggering and other important bird species in the IBA Tikveš Region Tabela 29: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Tikveško okrožje Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2009 2 A A1 Coracias garrulus B 2009 5-15 C A1 Falco naumanni B 2003 230-250 B B2 Accipiter brevipes B 2009 2-3 C B2? Buteo rufinus R 2010 2-4 C B2? Ardea cinerea B 2001-2010 60-90 A N Falco biarmicus B 2007 1-2 B N Circaetus gallicus B 2008 3-5 B N Aquila heliaca R 2010 1-2 B N Aquila chrysaetos R 2009 1-2 A N Bubo bubo R 2009 2-4 B N Figure 19: Map of the IBA Tikveš Region with its main features depicted Slika 19: Zemljevid IBA Tikveško okrožje z glavnimi značilnostmi območja Figure 20: Characteristic landscape of the IBA Tikve{ Region (photo: M. Velevski) Slika 20: Zna~ilna krajina IBA Tikve{ko okrožje (foto: M. Velevski) national colony of Grey Heron Ardea cinerea (60-90 pairs) (Table 29). Habitats and land use The greater part of the site is used for agriculture — vineyards and orchards dominate, although dry pastures (steppe-like grasslands) and remains of oak scrubs are well-represented (Table 30, Figure 20). Threats Documented cases of Griffon Vultures Gyps fulvus being poisoned exist from the past, with the most prominent single event of poisoning taking place in 1993 at the Dubrovo dump site, when ca. 60-70 individuals of Egyptian Vultures were poisoned during deratization of the dump site just prior to their migration (Grubač 1997). Pesticide use is likely, as well as hunting; poaching is also present. Livestock Table 30: The main CORINE land cover types (Level 3) in the IBA Tikve{ Region Tabela 30: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Tikve{ko okrožje Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 211 Non-irrigated arable land 14.0 242 Complex cultivation patterns 29.0 243 Land principally occupied by agriculture, with significant areas of natural vegetation 9-2 231 Pastures 13.0 221 Vineyards 7-8 321 Natural grasslands 14.0 324 Transitional woodland-shrub 9-1 Other 4.0 Table 31: The main threats to birds and their importance in the IBA Tikve{ Region Tabela 31: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Tikve{ko okrožje Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 110 Use of pesticides high F. naumanni, C. garrulus 243 Trapping, poisoning, poaching high A. heliaca, G. fulvus, N. percnopterus 141 Abandonment of pastoral systems medium F. naumanni, N. percnopterus, G. fulvus 511 Electricity lines medium F. naumanni, A. heliaca, C. garrulus 502 Motorways, roads medium A. heliaca, C. garrulus, F. naumanni breeding has decreased, very likely impacting vulture populations in the area (Table 31). Conservation Site is not protected, and no conservation measures are ongoing. 3.2.9. Pčinja - Petrošnica - Kriva Reka Rivers General information Name in English: Pčinja - Petrošnica - Kriva Reka Rivers Name in Macedonian: Reka Pčinja - reka Petrošnica -Kriva Reka (peKa n^H^a - peKa neTpomH^a - KpuBa PeKa) IBA code: MK014 Criteria: A1, A3, B2 Area: 84,938 ha Central coordinates: 21o55'48.62"E, 42o10'2.20"N Altitude: 280-1,355 m a.s.l. Administrative region(s): Kumanovo, Staro Nagoričane, Kratovo, Probištip, Rankovce Site description Situated in the northern part of the country, this large IBA includes three geographically and ecologically different areas of significant ornithological value. Starting from the border with Serbia north of Kumanovo (near Sopot village), the boundary runs south avoiding the town of Kumanovo and its nearest villages, crosses the Pčinja River south this town (at the village of Pčinja), continues eastwards following the motorway from Kumanovo to Sveti Nikole and through villages of K'šanje and Tatomir, turns north below the peak of Gradište (1,009 m a.s.l.) and continues through Filipovci and Železnica villages near Kratovo. It continues north through the villages of Opila and Rankovce, and then turns NW, until passing through Arbanaško village and reaching the national border again. The site adjoins the site "Pcinja" in Serbia (SER025 in Heath & Evans 2000, but RS036 in Puzovic et al. 2009), forming a trans-boundary IBA. The site embraces medium-size mountains, most dominant being Mt Kozjak in the north (summit Figure 21: Map of the IBA P~inja - Petrošnica - Kriva Reka Rivers with its main features depicted Slika 21: Zemljevid IBA Reke P~inja - Petrošnica - Kriva reka z glavnimi zna~ilnostmi obmo~ja 216 Table 32: List of triggering and other important bird species in the IBA P~inja - Petrošnica - Kriva Reka Rivers Tabela 32: Seznam kvalifikacijskih in drugih pomembnih vrst v IBA Reke P~inja - Petrošnica - Kriva reka Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2008-2010 2-4 A A1, B2 Aquila heliaca R 2010 4-6 A A1, B2 Coracias garrulus B 2007 5-20 C A1 Ficedula semitorquata B 2009 20-50 C A1 Alectoris graeca R 2009 30-100 C A3, B2 Lanius nubicus B 2008 10-30 C A3, B2 Oenanthe hispanica B Frequent A3 Hippolais olivetorum B Frequent A3 Sylvia cantillans B Common A3 Sitta neumayer R Common A3 Emberiza melanocephala B Common A3 Ciconia nigra B 2008 3-4 A B2 Circaetus gallicus B 2008 10-15 C B2 Buteo rufinus R 2010 12-15 B B2 Falco naumanni B 2010 10-50 C B2 Falco biarmicus B 2009 3-4 B B2 Bubo bubo R 2007 5-10 C B2 Falco vespertinus P 2008 5-50 ind. C A1? Falco tinnunculus R Common B2? Gyps fulvus N 2008 -Ö - 2 C N Aquila chrysaetos R 2010 1-2 C N Falco peregrinus R 2010 3-5 C N Burhinus oedicnemus B 2011 10-20 N Virovi 1,285 m a.s.l.), and the highest peaks towards Mt German in the east (Tabla summit 1,355 m a.s.l.). The geological composition is diverse, with predominating metamorphic rocks of different ages. Main rivers are the Kriva Reka with its tributary Kratovska Reka, and the Pčinja with the Bistrica and Petrošnica being its main tributaries (Figure 21). Species The mosaic landscape of steppe-like pastures and woods intersected with river valleys and small gorges attracts very large number of species, including raptors and seven species characteristic of the Mediterranean biome, some ofwhich (Masked Shrike, Rock Nuthatch) reach here the northernmost part of their distribution areas in the Central Balkans. Large portions of the site have been insufficiently studied, making the estimate of population sizes difficult, and thus in most cases the figures given should be considered conservative. Some of the species (e.g. Egyptian Vulture, Imperial Eagle) have undergone a notable decline in the last decade (GrubaČ & Velevski in prep.), but other important species seem to have increased in numbers, especially the Lesser Kestrel (10-50 pairs), for the first time recorded breeding in small colonies in the villages in 2010 (M. Ružic pers. comm.). Notable is the breeding density of the Semicollared Flycatcher (20-50 pairs) in the northernmost parts of the site, reaching 6 pairs/5 ha in the remaining patches of mature Beech forests (Skorpi'kova et al. 2009B), and further studies on distribution and population size of this species here are urgently needed. Other species that is likely to meet the thresholds set for populations of European importance is Common Kestrel. Small migrating flocks of Red-footed Falcons have also been observed (Table 32). Historically, breeding of Griffon Vultures has been recorded (B. Grubač unpubl.) Habitats and land use Very complex mosaic of habitat types is found at this site, from bare limestone cliffs in the gorges and bare silicate cliffs both in gorges and mountains, to old Beech and oak forests. Poplar and willow belts are found along all major rivers. Extensive arable fields Figure 22: Characteristic landscape of the IBA P~inja - Petrošnica - Kriva Reka Rivers (photo: B. Rubini}) Slika 22: Zna~ilna krajina IBA Reke P~inja - Petrošnica - Kriva reka (foto: B. Rubini}) and dry pastures are present, especially in the southern part of the site, while the northern part is dominated by oak forest remains on silicate, often exposed bedrock (Table 33, Figure 22). Table 33: The main CORINE land cover types (Level 3) in the IBA P~inja - Petrošnica - Kriva Reka Rivers Tabela 33: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v IBA Reke P~inja - Petrošnica - Kriva reka Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 211 Non-irrigated arable land 15.0 242 Complex cultivation patterns 17.5 243 Land principally occupied by 10.4 agriculture, with significant areas of natural vegetation 231 Pastures 28.5 311 Broad-leaved forest 8.2 324 Transitional woodland-shrub 18.0 Other 2.4 Threats Serious threat to the large raptors is the planned wind farm along the borderline with Serbia. Construction of railway and highway from Kumanovo to the Bulgarian border will possibly impact the breeding pairs of Imperial Eagles, Long-legged Buzzards, Black Stork, Lanner Falcon, and others. Forestry practices unfavourable to the Semicollared Flycatcher are likely. Hunting is widespread, poaching probably takes place, and occasional use of poisonous baits has been noted. Interest by falconers, especially in Lanner Falcon nests, exist, although no nest robbery has been documented so far. As in other regions of the country, livestock reduction has probably impacted vultures and Imperial Eagles (Table 34). Conservation Only an insignificant portion (less than 1%) of the site has been protected within three separate sites (Orašac, Kuklica and Ploče - Litotelmi), on locations without significant importance for birds. Large part of the IBA overlaps the proposed Emerald Site "German - Pčinja" (MK0000029). Table 34: The main threats to birds and their importance in the IBA Pčinja - Petrošnica - Kriva Reka Rivers Tabela 34: Najpomembnejši dejavniki ogrožanja ptic in njihov vpliv v IBA Reke Pčinja - Petrošnica - Kriva reka Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 141 Abandonment of pastoral systems high N. percnopterus, F. naumanni, G. fulvus 243 Trapping, poisoning, poaching high A. heliaca, N. percnopterus 230 Hunting medium A. graeca 160 General forestry management medium F. semitorquata 242 Taking from nest (falcons) medium F. biarmicus 410 Industrial or commercial areas medium N. percnopterus, B. rufinus, A. chrysaetos, F. vespertinus 502 Motorways, roads medium C. nigra, A. heliaca, F. biarmicus, B. rufinus 503 Railway lines, TGV medium A. heliaca, B. rufinus, C. garrulus 701 Water pollution medium C. nigra 3.2.10. Preod - Gjugjance Name in English: Preod - Gjugjance Name in Macedonian: Preod - Gjugjance (npeog - TyraH^) IBA code: MK015 Criteria: A1, B2 Area: 10,893 ha Central coordinates: 21o58'9.22"E, 4lo57'32.02"N Altitude: 320-776 m a.s.l. Administrative region(s): Sveti Nikole, Probištip, Kumanovo Site description The site is situated in central Macedonia, north of the town Sveti Nikole. Starting from Nemanjica village, the boundary runs NE following the slopes of Mt Mangovica to the village Gorno Barbarevo. Part of this boundary is shared with the Zletovska River Valley site (MK012). From Gorno Barbarevo, the boundary turns west to Kokošinje village, and then continues S-SW to the villages of Stanjevci and Alakince, following the road Kumanovo-Sveti Nikole for a few kilometres. From Alakince, it roughly follows the 400 m isohypse to the village of Preod, from where it turns east to the village of Nemanjica again. The site is characterized by low mountainous relief as part of Mt Mangovica, with geological composition dominated by metamorphite and magmatites, while lake sediments are found in the lower parts. The largest river is the Karataš (Figure 23). Species The site has been insufficiently studied, but 2-3 pairs of Imperial Eagle are found, breeding on the slopes of the hills and in the fields, together with 30-50 pairs of Lesser Kestrel breeding in the villages of the region. Rollers are also present, but their population was not censused. Other important species include Golden Eagle and possibly single pairs of Black Stork Ciconia nigra and Egyptian Vulture Neophron percnopterus (Table 35). General information Table 35: List of triggering and other important bird species in the IBA Preod - Gjugjance Tabela 35: Seznam kvalifikacijskih in drugih pomembnih vrst v IBA Preod - Gjugjance Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Aquila heliaca R 2007 2-3 B A1 Falco naumanni B 2003 30-50 B B2 Coracias garrulus B Frequent N Circus pygargus B 2010 3-10 B N Aquila chrysaetos R 2010 1 A N Figure 23: Map of the IBA Preod - Gjugjance with its main features depicted Slika 23: Zemljevid IBA Preod - Gjugjance z glavnimi zna~ilnostmi obmo~ja Table 36: The main CORINE land cover types (Level 3) in the IBA Preod - Gjugjance Tabela 36: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Preod - Gjugjance Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 211 Non-irrigated arable land 25.4 242 Complex cultivation patterns 12.8 243 Land principally occupied by 16.6 agriculture, with significant areas of natural vegetation 231 Pastures 18.9 311 Broad-leaved forest 4.5 324 Transitional woodland-shrub 21.8 Habitats and land use Agricultural arable land predominates, although wet meadows and pastures are also present in fairly high percentages. Remains of oak forests and wind-protection tree-rows are found, on some places forming real forest stands (Table 36, Figure 24). Threats Wind farm development is planned in the near future within this region, which will also affect the sites of Zletovska River Valley (MK012) and Ovče Pole (MK019). Planned highway connecting Skopje with Stip will cross the site. Also, construction of a new cargo airport is foreseen in more distant future. Other threats are poorly documented. Electricity lines at the site have proved to be the cause of Lesser Kestrel mortalities due to electrocution, although other important species are likely to be affected as well. Livestock numbers have been greatly reduced in numbers, resulting in lower food availability for Imperial Eagles and foraging vultures, but also in overgrown pastures (i.e. breeding sites of Stone Curlew being lost) (Table 37). Conservation The site is not protected. Figure 24: Characteristic landscape of the IBA Preod - Gjugjance (photo: M. Velevski) Slika 24: Zna~ilna krajina v IBA Preod - Gjugjance (foto: M. Velevski) Table 37: The main threats to birds and their importance in the IBA Preod - Gjugjance Tabela 37: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Preod - Gjugjance Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 141 Abandonment of pastoral systems high F. naumanni 511 Electricity lines high A. heliaca, F. naumanni, C. garrulus 410 Industrial or commercial areas medium A. heliaca, F. naumanni 502 Motorways, roads medium A. heliaca, F. naumanni, C. garrulus 505 Airport medium A. heliaca, F. naumanni, C. garrulus Site description Situated east of the town Probištip in NE Macedonia, the site includes the lower western slopes of Mt Osogovo. Starting at the town Zletovo, the boundary runs east to the village of Tursko Rudare, to the locality Preslop, surrounds the Pasadžikova Čuka peak (1,544 m a.s.l.), continues north to the Ponikva ridges, west to Panagjur (1,669 m a.s.l.) and Kula (1,391 m a.s.l.), passes through the village Jamište, crosses the Zletovska Reka River and reaches Lukovo village, from where it continues south passing between the villages of Dobrevo and Lesnovo, reaching Zletovo again. The relief is intersected by several river valleys, i.e. 3.2.11. Osogovo Mountains General information Name in English: Osogovo Mountains Name in Macedonian: Osogovski Planini (OcoroBCKH n^aHHHH) IBA code: MK016 Criteria: A1, B2 Area: 7,530 ha Central coordinates: 22°17T2.8"E, 42o01'6.86"N Altitude: 400-1,669 m a.s.l. Administrative region(s): Probištip, Kočani, Kratovo Figure 25: Map of the IBA Osogovo Mountains with its main features depicted Slika 25: Zemljevid IBA Osogovsko gorovje z glavnimi zna~ilnostmi obmo~ja Zletovska Reka, Štalkovačka (Stara) Reka, Zelengradska Reka, Jamiška Reka. The largest cliffs are those of Ratkova Skala (Stara Reka Gorge). Geologically, magmatic rocks prevail in the region (Figure 25). Species Triggering species for the site are the Lanner Falcon (two pairs) and Egyptian Vulture (one pair; in 1990s, four territories were known, B. Grubač unpubl.). Two Table 38: List of triggering and other important bird species in the IBA Osogovo Mountains Tabela 38: Seznam kvalifikacijskih in drugih pomembnih ptic v IBA Osogovsko gorovje Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2010 1 A A1 Falco biarmicus B 2007 2 A B2 Ciconia nigra B 2008 1 A N Circaetus gallicus B 2008 2 A N Buteo rufinus B 2009 1 A N Aquila chrysaetos R 2008 1 A N Falco peregrinus R 2008 3 A N Alectoris graeca R Frequent N Bubo bubo R 2008 1-2 C N Ficedula semitorquata B 2009 0-20 C Figure 26: Characteristic landscape of the IBA Osogovo Mountains (photo: M. Velevski) Slika 26: Zna~ilna krajina IBA Osogovsko gorovje (foto: M. Velevski) Table 39: The main CORINE land cover types (Level 3) in the IBA Osogovo Mountains Tabela 39: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Osogovsko gorovje Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 231 Pastures 9.2 311 Broad-leaved forest 53.2 324 Transitional woodland-shrub 26.8 Other 10.8 breeding pairs of Short-toed Eagle, 1—2 pairs of Eagle Owl, single pairs of Black Stork, Long-legged Buzzard and Golden Eagle, and three pairs of Peregrine Falcons have also been found. Semicollared Flycatcher has been recorded breeding at scattered localities on Mt Osogovo, although in numbers probably insufficient to include large territories of the mountain within the IBA's boundaries. The species has not yet been recorded within the site's boundaries, but is very likely present (Table 38). Until 2003, a small colony of Griffon Vultures used to breed here (E. Stoynov & E. Lisicanec, unpubl.). Habitats and land use The area is forested; oak and Beech forests alternate depending on the exposition. On some locations, forests are well preserved, with stands of mature trees present. The cliff complex, composed of several smaller and one dominant cliff, defines the landscape. The valley of Zletovska Reka River has a good deal of eroded surfaces and scrubs in different stages of succession (Table 39, Figure 26). Threats The local population is highly dependent on natural resources (pastures, forests) for survival, resulting in Table 40: The main threats to birds and their importance in the IBA Osogovo Mountains Tabela 40: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Osogovsko gorovje Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 160 General forestry management high F. semitorquata 242 Taking from nest (falcons) high F. biarmicus, F. peregrinus 403 Dispersed habitation medium C. nigra 502 Motorways, roads medium C. nigra, N. percnopterus 301 Quarries medium C. nigra, N. percnopterus, F biarmicus, F peregrinus high timber extraction and collection of secondary forest products. Forestry is intensive, and clearcutting is frequently practiced. Mineral extraction took place in the past. A road connecting Zletovo with the "Ponikva" tourist locality is planned to pass through this site. Nest robbery (Lanner) has been noted (Table 40). Conservation Part of the site is managed as a hunting ground for big game, with limited access and thus under somewhat lesser pressure than the surrounding. The site completely falls within the borders of the Emerald Site (MK0000026) and the proposed protected area "Osogovo Mountains". 3.2.12. Jakupica Mountain General information Name in English: Jakupica Mountain Name in Macedonian: Jakupica (JaKyn^a) IBA code: MK017 Criteria: A3, B2 Area: 23,081 ha Central coordinates: 21o19'31.49"E, 4lo45'10.59"N Altitude: 470-2,539 m a.s.l. Administrative region(s): Sopište, Studeničani, Čaška, Makedonski Brod, Želino Site description This IBA occupies the highest parts of Mt Jakupica (most of the site lies above 1,600 m a.s.l.) in central Macedonia. Its boundary starts at Kula locality south of Skopje, descends into the Oča River Valley by following the road through the abandoned village of Kapina, then follows the Oča upstream and SE to the Jaloarnik locality, then follows the 1,200 m isohypse south to just above the village of Belica, then ascends to the isohypse of 1,600 m. This isohypse forms almost Figure 27: Map of the IBA Jakupica Mountain with its main features depicted Slika 27: Zemljevid IBA Gora Jakupica z glavnimi zna~ilnostmi obmo~ja the entire southern boundary (except the Odbivarnik locality) and a large part of the eastern boundary to Kurtovica, where it ascends to 1,800 m a.s.l. Following this isohypse, the boundary continues north, to the saddle between Gorni and Dolni Pepeljak, follows the ridge Dolni Pepeljak and descends into the valley of Table 41: List of triggering and other important bird species in the IBA Jakupica Mountain Tabela 41: Seznam kvalifikacijskih in drugih pomembnih vrst v IBA Gora Jakupica Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Prunella collaris B 2002 20-40 C A3 Tichodroma muraria B 1999 5-10 C A3 Pyrrhocorax graculus B 2010 100-150 B A3 Montifringilla nivalis B Rate A3 Aquila chrysaetos R 1999 3-4 B B2 Alectoris graeca R 2010 50-100 C B2 Falco tinnunculus R Common B2? Falco peregrinus R 2010 2-3 C N Bubo bubo R 2010 4-8 C N Eremophila alpestris balcanica B Frequent N Pyrrhocorax pyrrhocorax B Frequent N the Patiška Reka River. From here it turns west and near Kopanje reaches Kula again. High mountain karst fields (Begovo Pole, Solunsko Pole, Silegarnik) are the area's main geomorphologic feature. The highest peaks are Karadžica (2,473 m a.s.l.), Ubava (2,344 m a.s.l.) and Solunska Glava Mts (2,539 m a.s.l.). Most prominent in the NW part are the cliffs of Mt Karadžica, while in the south the distinctive cliffs Nežilovski Steni are dominant. Geological composition is of Precambrian dolomites and dolomite marbles (Figure 27). Species Parts of the site have been well studied (within wider boundaries, except the western slopes), and about 120 species have been recorded so far (Dimovski 1967, Velevski et al. 2002b). The main reason for its designation are species characteristic of the Eurasian high-montane biome, found here in significant numbers, usually inhabiting the cliffs above 1,800 m a.s.l. This is the third most important site in the Table 42: The main CORINE land cover types (Level 3) in the IBA Jakupica Mountain Tabela 42: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Gora Jakupica Code/ Koda CORINE land cover type/ tip pokrovnosti in rabe tal Coverage/ Pokrovnost (%) 311 Broad-leaved forest 10.7 312 Coniferous forest 11.3 313 Mixed forest 10.7 332 Bare rocks 0.7 321 Natural grasslands 49.9 322 Moors and heathland 2.6 324 Transitional woodland-shrub 12.7 Other 1.4 country after Sar Planina Mountain (MK001) and the Radika River Catchment (MK002). From this group of birds, presence of the Snowfinch, a very rare Table 43: The main threats to birds and their importance in the IBA Jakupica Mountain Tabela 43: Najpomembnejši dejavniki ogrožanja ptic in njihov vpliv v IBA Gora Jakupica Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 141 Abandonment of pastoral systems high P. graculus 243 Trapping, poisoning, poaching high A. chrysaetos 960 Interspecific faunal relations high A. chrysaetos, B. bubo 230 Hunting medium A. graeca Figure 28: Characteristic landscape of the IBA Jakupica Mountain (photo: S. Hristovski) Slika 28: Zna~ilna krajina v IBA Gora Jakupica (foto: S. Hristovski) species here, has also been recorded (Dimovski 1967, Matvejev 1976). Although it has not been recorded since then, we have included it in the list. The site also holds important populations of Red-billed Chough and Shore Lark. Golden Eagle population (3-4 pairs) meets the threshold of European importance. The site holds internationally important population of Rock Partridge (50-100 pairs), and probably Common Kestrel, but their relative importance against other sites in Macedonia is unknown (Table 41). Habitats and land use Alpine pastures, moors, some heathland and large rocky karst fields dominate above the tree zone, with limestone cliff-faces descending steep into the forests (Beech Fagus sylvatica in the south, European Black Pine Pinus nigra in the west). Large complexes of Mountain Pine Pinus mugo are found in the northern part of the site. Beech forest is the dominant broad-leaved forest, often mixed with Bulgarian Fir Abies borisii-regis or Black Pine (Table 42, Figure 28). Threats Apart from hunting and poaching, further resulting in the reduction of raptor prey base, no other direct threats have been recorded. Livestock breeding has significantly decreased, probably impacting populations of Choughs and large raptors (Table 43). Conservation The site is partially included in the Multipurpose protected area "Jasen", which due to its intensive management and significant conservation efforts reduces the threats from hunting and poaching (even though controlled hunting activities are implemented by the "Jasen" management). Small parts of the site are included in the "Belešnička Reka" Nature Monument. A small protected area for the conservation ofMountain Pine (Juričica) was also designated within the site. Designation of a new national park, "Jakupica", is planned, which is to include the remaining territory. The site is entirely included in the "Jakupica" Emerald Site (MK0000017). 3.2.13. Taor Gorge General information Name in English: Taor Gorge Name in Macedonian: Taorska Klisura (TaopcKa K^Hcypa) IBA code: MK018 Criteria: A1, A3 Area: 2,538 ha Central coordinates: 21o42'46.55"E, 41o46'37.19"N Altitude: 170-675 m a.s.l. Administrative region(s): Veles Site description The site occupies a short section of the Vardar River Valley (southernmost parts of the entire Taor Gorge) north of Veles in central Macedonia and within its borders includes the hills that are close to the Valley, as well as the locality Kalište to the north and the locality Sredno Brdo to the south (Figure 29). The geological composition is very diverse, belonging to the complex Vardar tectonic zone, with carbonates, metamorphic and magmatic rocks from different periods. Table 44: List of triggering and other important bird species in the IBA Taor Gorge Tabela 44: Seznam kvalifikacijskih in drugih pomembnih vrst v IBA Soteska Taor Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2007-2010 1-2 A A1 Alectoris graeca R 2009 10-20 C A3 Oenanthe hispanica B Common A3 Sylvia cantillans B Common A3 Sitta neumayer R Common A3 Lanius nubicus B Frequent A3 Emberiza melanocephala B Common A3 Ciconia nigra B 2008 0-1 B Circaetus gallicus B 2008 1-2 B N Buteo rufinus R 2009 2 A N Aquila heliaca R 2009 0-1 B Aquila chrysaetos R 2010 0-1 B Falco peregrinus R 2009 1-2 B N Bubo bubo R 2008 2-3 B N Coracias garrulus B 2009 2-5 C N Table 45: The main CORINE land cover types (Level 3) in the IBA Taor Gorge Tabela 45: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Soteska Taor Code/ CORINE land cover type/ Koda tip pokrovnosti in rabe tal Complex cultivation patterns Land principally occupied by agriculture, with significant areas of natural vegetation Pastures Broad-leaved forest Sparsely vegetated areas Transitional woodland-shrub Other Coverage/ Pokrovnost (%) 242 243 231 311 333 324 4.6 7.1 21.7 18.0 2.8 43.5 2.4 Species The Egyptian Vulture (1-2 pairs) and a group of six species characteristic of the Mediterranean biome with significant populations meet the criteria for designation of the site as an IBA. One of the two pairs of Egyptian Vultures has not been observed since 2008 and might have been lost recently. Other important species include Eagle Owl (2-3 pairs), Long-legged Buzzard (2 pairs), Peregrine Falcon (1-2 pairs), Golden Eagle (1 pair), Black Stork (possibly one pair), and possible breeding of Imperial Eagle. A few pairs of Rollers have also been recorded (Table 44). Figure 29: depicted Map of the IBA Taor Gorge with its main features Slika 29: Zemljevid IBA Soteska Taor z glavnimi zna~ilnostmi obmo~ja Figure 30: Characteristic landscape of the IBA Taor Gorge (photo: M. Velevski) Slika 30: Značilna krajina IBA Soteska Taor (foto: M. Velevski) Table 46: The main threats to birds and their importance in the IBA Taor Gorge Tabela 46: Najpomembnejši dejavniki ogrožanja ptic in njihov vpliv v IBA Soteska Taor Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 960 Interspecific faunal relations high A. chrysaetos, B. bubo, A. heliaca 410 Industrial or commercial areas high N. percnopterus, C. nigra, B. rufinus, C. garrulus 502 Motorways, roads high N. percnopterus 162 Artificial planting medium B. rufinus 230 Hunting medium A. graeca 301 Quarries medium B. rufinus, F. peregrinus 501 Paths, tracks, cycling tracks medium C. nigra 503 Railway lines, TGV medium N. percnopterus, C. nigra, B. rufinus 530 Improved access to site medium N. percnopterus, C. nigra, B. rufinus 701 Water pollution medium C. nigra 220 Leisure fishing medium C. nigra Habitats and land use The most important habitats for birds are the two limestone cliffs, surrounded by pastures, remains of oak forests and scrubland, and divided by the Vardar River and its riparian willow belt (Table 45, Figure 30). Threats Stone mining activities are taking place in the site's close surrounding, and expansion of these activities into the site is possible. Construction of a hydro-power plant is planned, with reservoir that will submerge parts of the habitats. Construction will require translocation to the dirt road under the peak of Struga (758 m a.s.l.) at the village of Dolno Barbarevo. From here it shares its boundary with the Preod - Gjugjance site (MK015) SW of Nemanjica village. Then it continues south to the irrigation channel, follows it westwards to the town of Sveti Nikole, avoiding it from the south and proceeding SW to the villages of Gjuzemelci, Sojaklari and Otovica. From here it continues southwards, following the E-75 highway (Veles-Skopje), until reaching its starting point east of Veles (Figure 31). The site is a tectonic valley, limited by Mt Mangovica, Bogoslovec Hill and the Vardar River. Geologically, it consists mostly of Pliocene lake sediments. Species No complete checklist of the birds of this area exists. Historically, the site was an important breeding place for the Black Vulture Aegypius monachus (Karaman 1929) and Little Bustard Tetrax tetrax (Stresemann 1920). The former has not been recorded in the wider region since 1960s (Dimovski 1971A), while the last record of four Little Bustard individuals originates from the place Domus Bunar near the village of Crnilište in 1972 (Trpkov et al. 1978). The most important breeding species are the Imperial Eagle (10-12 pairs), Lesser Kestrel (200250 pairs), and Roller (10-30 pairs). The Imperial Eagles breed in trees and on electricity pylons often close to human settlements. Lesser Kestrels are found breeding exclusively in the villages, aggregating in large numbers (flocks of 300 ind. were seen on 13 Sep 2006, M. Velevski unpubl.) prior to their migration. The region is frequently used by foraging Griffon and Egyptian Vultures, the former arriving from the colonies at Mariovo, Tikveš Lake and Demir Kapija, Table 47: List of triggering and other important bird species in the IBA Ov~e Pole Tabela 47: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Ov~e Pole Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Aquila heliaca R 2010 10-12 A A1, B2 Coracias garrulus B 2006 I0-30 C A1, B2 Neophron percnopterus N 2009 6-10 ind. A A1 Falco naumanni B 2003 200-250 A B2 Burhinus oedicnemus B 2010 20-50 C B2 Lanius minor B 2009 30-I00 C B2 Gyps fulvus N 2008 5-20 ind. A N Circaetus gallicus B 2009 2-4 C N Buteo rufinus R 2010 2-3 B N Falco cherrug B 2010 0-1 C of the existing railway closer to the cliffs. The existing highway and its maintenance cause much disturbance. Afforestation with allochthonous tree species is taking place (Table 46). Conservation Establishment of a protected area is planned. The site partially overlaps the "Katlanovo -Taor" Emerald Site (MK0000030). 3.2.14. Ovče Pole General information Name in English: Ovče Pole Name in Macedonian: Ovče Pole (OBHe nojje) IBA code: MK019 Criteria: A1, B2 Area: 48,183 ha Central coordinates: 22o00'1.33"E, 41o49'1.47"N Altitude: 230-707 m a.s.l. Administrative region(s): Veles, Lozovo, Sveti Nikole, Probištip, Karbinci, Štip, Gradsko Site description This large plain is situated in central Macedonia, with the site boundary starting near the town of Veles, going more or less eastwards towards the village of Kišino, then NE by following the ridges of small hills and ravines, till it reaches the village Bogoslovec. Then it continues SE to the village of Dobrošani, where it continues east to Suševo, north to Sarčievo, NE to Gorni Balvan, and again north to Pišica. From here it shares its boundary with the Zletovska River Valley site (MK012), going NW along the ridge of Mangovica Mt 2v45e 2t50e 21'55'e 22'cte 22'5'e 22'10'e 22'15'e Figure 31: Map of the IBA Ov~e Pole with its main features depicted Slika 31: Zemljevod IBA Ov~e Pole z glavnimi zna~ilnostmi obmo~ja Table 48: The main CORINE land cover types (Level 3) in the IBA Ov~e Pole Tabela 48: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Ov~e Pole Code/ Koda CORINE land cover type/ tip pokrovnosti in rabe tal Coverage/ Pokrovnost (%) 211 Non-irrigated arable land 44.9 242 Complex cultivation patterns 15.2 243 Land principally occupied by agriculture, with significant areas of natural vegetation 3.6 231 Pastures 15.4 112 Discontinuous urban fabric 0.4 311 Broad-leaved forest 1.4 333 Sparsely vegetated areas 0.2 324 Transitional woodland-shrub 14.7 Other 3.9 and the latter from the breeding sites at Bregalnica. Subadult individuals, however, have also been observed. Juvenile and immature Imperial Eagles are present in the wintering period as well (Table 47). Habitats and land use Ovče Pole is a large plain, almost entirely used for agriculture, with exception of small unsuitable salty patches and some remains of wetlands. In the peripheral parts dry pastures dominate. Tree stands with large poplar or oak trees are scattered throughout the site. Several villages are embedded in the landscape (Table 48, Figure 32). Threats Poisonous baits are occasionally used, resulting in poisonings of Griffon Vultures and Imperial Eagles, with the last major incident occurring in 2003 (14 Griffon Vultures and at least one Imperial Eagle found dead, T. Lisicanec, E. Lisicanec & B. Hallman unpubl.). The plains were the most important wintering grounds for sheep in Macedonia, but their numbers have significantly decreased. Pesticide use is probably widespread due to intensive agriculture. Hunting is Figure 32: Characteristic landscape of the IBA Ov~e Pole (photo: M. Velevski) Slika 32: Zna~ilna krajina v IBA Ov~e Pole (foto: M. Velevski) Table 49: The main threats to birds and their importance in the IBA Ov~e Pole Tabela 49: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Ov~e Pole Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 110 Use of pesticides high C. garrulus, F. naumanni 141 Abandonment of pastoral systems high G. fulvus, N. percnopterus 511 Electricity lines high A. heliaca, F. naumanni, C. garrulus 243 Trapping, poisoning, poaching high A. heliaca, G. fulvus 161 Forest planting medium B. oedicnemus 230 Hunting medium A. heliaca 290 Hunting, fishing or collecting activities not referred to above medium A. heliaca 410 Industrial or commercial areas medium G. fulvus, N. percnopterus, A. heliaca intensive, especially of Grey Partridge Perdix perdix and Quail Coturnix coturnix, and possible risks from disturbance and secondary lead poisoning exist for the Imperial Eagles. Poaching also takes place. The threat from low and medium tension electricity poles is still unknown, but is very likely. Destruction of Imperial Eagle nests on electricity pylons, where they breed, used to take place by the State electro-distribution company. Wind farms to be erected in the future south of Stip and north of Sveti Nikole will likely impact the Imperial Eagle population and foraging vultures (Table 49). Conservation The site is not protected, but has been proposed as an Emerald Site (MK0000035). Figure 33: Map of the IBA Topolka - Babuna - Bregalnica Rivers with its main features depicted Slika 33: Zemljevid IBA Reke Topolka - Babuna - Bregalnica z glavnimi značilnostmi območja 3.2.15. Topolka - Babuna - Bregalnica Rivers Name in English: Topolka - Babuna - Bregalnica Rivers Name in Macedonian: Reka Topolka - reka Babuna - reka Bregalnica (PeKa Tonoma - peKa EaSyHa - peKa Eper&m^a) IBA code: MK020 Criteria: A1, A3, B2 Area: 27,648 ha Central coordinates: 21o54'27.65"E, 4lo40'43.23"N Altitude: 150-755 m a.s.l. Administrative region(s): Veles, Gradsko, Lozovo, Negotino, Štip, Sveti Nikole Site description This site unites two former IBAs in central Macedonia: the "Babuna Gorge, Topolka Gorge, and Crn Kamen" (MK003) and "Bregalnica River" (MK004) (Heath & Evans 2000), connecting them with the ecologically similar valley of the Vardar River in its middle section. The boundary starts south of Veles, continues west through Prevalec settlement and turns south of the Topolka River Gorge and Bair Hill. When passing the village of Gorno Orizari, it crosses the Topolka and Babuna Rivers and continues south across the peaks of Dabovic (619 m a.s.l.), Seir (677 m a.s.l.) and Krvenik (854 m. a.s.l.). From here it continues east, passing the village of Grnčište and crossing the pass under peak Cucula (469 m a.s.l.), reaching the Vardar River at the village of Nogaevci and following the river south until the village of Ulanci. From here it continues NE through Cucule, Rajnički Rid and Bunarče, then turns north to Kara Tepe. By following small ridges and ravines, it reaches the valley of the rivulet Kuri Dere, from where it continues NE till the Bregalnica River. It follows the river north to Dobrošani village, where it meets the boundary of the Ovče Pole site (MK019), following it at first NW (till Bogoslovec village), then SW to Kišino village, and west to Veles. Dominant reliefs are the hills and gorges of the Babuna, Topolka and Bregalnica Rivers and their highly typical meanders (Figure 33). Mesozoic General information Table 50: List of triggering and other important bird species in the IBA Topolka- Babuna-Bregalnica Rivers Tabela 50: Seznam kvalifikacijskih in drugih pomembnih vrst v IBA Reke Topolka- Babuna-Bregalnica Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2010 4 A A1, B2 Aquila heliaca R 2010 3-5 B A1, B2 Coracias garrulus B 2009 20-40 C A1, B2 Alectoris graeca R 2010 30-100 C A3, B2 Lanius nubicus B 2010 50-150 B A3, B2 Oenanthe hispanica B Abundant A3 Hippolais olivetorum B Frequent A3 Sylvia cantillans B Abundant A3 Sitta neumayer R Frequent A3 Emberiza melanocephala B Abundant A3 Circaetus gallicus B 2009 5-10 B B2 Buteo rufinus R 2009 7-10 B B2 Falco biarmicus B 2009 3-4 A B2 Burhinus oedicnemus B 2009 20-50 C B2 Bubo bubo R 2009 6-10 C B2 Monticola solitarius B 2003-2010 20-50 C B2 Ciconia nigra B 2009 1 A N Gyps fulvus N 2009 5-20 ind. A N Aquila chrysaetos R 2009 3 A N Accipiter brevipes B Rare N Falco naumanni B 2002 10 B N Falco peregrinus R 2009 3 A N formations prevail in the geological composition — Triassic, Jurassic and Cretaceous metamorphites, carbonates and magmatic rocks. West of the Vardar River, Eocene marine sediments are found. Species Parts of the site significantly differ in the level of knowledge about their bird fauna. Although the gorges of the Babuna River have been well known, attracting many ornithologists in the past (e.g. Stresemann 1920, Makatsch 1950, Bodenstein & Kroymann 1967-1969), who thus provided a number of data on the nearby gorge of the Topolka River, the valley and the gorge of the Bregalnica River have been completely unknown (and hardly accessible) till recently (Skorpi'kovä et al. 2006 & 2007), with the exception of studies of vultures in the 1980-1991 period (Grubač 1997), resulting in its identification as an IBA in the first inventory (Grimmett & Jones 1989). The site holds a large number of species triggering the IBA criteria, including three species of global conservation concern and several raptor species in good Table 51: The main CORINE land cover types (Level 3) in the IBA Topolka- Babuna-Bregalnica Rivers Tabela 51: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Reke Topolka - Babuna - Bregalnica Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 211 Non-irrigated arable land 12.9 242 Complex cultivation patterns 6.3 243 Land principally occupied by agriculture, with significant areas of natural vegetation 4.5 231 Pastures 32.9 333 Sparsely vegetated areas 1.7 321 Natural grasslands 12.9 324 Transitional woodland-shrub 23.7 Other 5.2 numbers. In the past, several Griffon Vulture breeding sites were known in gorges of all three main rivers (Vasic et al. 1985). Historically, the gorge of the Babuna River Figure 34: Characteristic landscape of the IBA Topolka - Babuna - Bregalnica Rivers (photo: M. Velevski) Slika 34: Zna~ilna krajina IBA Reke Topolka - Babuna - Bregalnica (foto: M. Velevski) was a breeding site of Lammergeier Gypaetus barbatus (Makatsch 1950). The Mediterranean bird assemblage is characterized by the exceptionally numerous populations of Black-eared Wheatear and Black-headed Bunting, while the Masked Shrike's population here is the largest in the country. Only one small colony (about 10 pairs) of Lesser Kestrels was found at the village of Orizari near Veles in 2002, although the species is numerous on both adjacent sites (MK019 & MK021). Other important species include the Black Stork, Levant Sparrowhawk and Golden Eagle (Table 50). Single historical data for Sardinian Warbler Sylvia melanocephala also exist, being the northernmost in the country (Rucner 1962-1964). Habitats and land use Large portion of the site is dominated by dry, steppelike pastures in different stages of succession towards oak forest, or planted with conifers. Two gorges (of the Babuna and Topolka Rivers) are found in Table 52: The main threats to birds and their importance in the IBA Topolka - Babuna - Bregalnica Rivers Tabela 52: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Reke Topolka - Babuna - Bregalnica Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 141 Abandonment of pastoral systems high G. fulvus, N. percnopterus 243 Trapping, poisoning, poaching high G. fulvus, N. percnopterus, A. heliaca 960 Interspecific faunal relations high A. chrysaetos, B. bubo, A. heliaca 100 Cultivation medium B. oedicnemus, C. garrulus 162 Artificial planting medium B. oedicnemus 230 Hunting medium A. graeca 403 Dispersed habitation medium C. nigra, A. heliaca 624 Mountaineering, rock climbing, speleology medium N. percnopterus, C. nigra 301 Quarries medium A. graeca, M. solitarius the western part, the first of which is particularly suitable for breeding of birds of prey due to large number of rock shelters and caves. The gorge of the Bregalnica River consists of sandstone, which is also full of suitable niches. Extensive agricultural fields are found especially in the surroundings of the village of Nogaevci. Riparian forest belts are dominated by Oriental Plane Platanus orientalis along the Babuna and Topolka, and poplar and willow trees along the Vardar and Bregalnica (Table 51, Figure 34). Threats The Topolka Gorge is threatened by the stone quarry planned to be expanded in near future, while opening of new quarries could badly impact the Babuna Gorge. Weekend cottages are becoming increasingly numerous in the Babuna Gorge; speleological and cliff-climbing activities are regular. Intensive robbery of Griffon Vulture nests has been recorded in the past (Vasic et al. 1985). The Vardar Valley and the Bregalnica River's surroundings are planted with allochthonous tree species, losing the steppe-like character. Intensive agriculture is taking place in and around the site. Along the Bregalnica, some traditional activities (capturing wild bees) cause problems to cliff-breeding raptors. Hunting, poaching and poison use still take place, resulting in direct losses (at least 10 Griffon Vultures poisoned in 2008, M. Velevski unpubl.) or prey base reduction. As elsewhere in Macedonia, livestock numbers have decreased a great deal (Table 52). Conservation Only a small paleontological locality (Karaslari) is under protection. Both Babuna Gorges and the Topolka Gorge have been proposed for protection. The Babuna - Topolka Gorges (MK0000023) and the Bregalnica Gorge (MK0000031) have also been proposed as Emerald Sites. 3.2.16. Gradsko - Rosoman - Negotino General information Name in English: Gradsko - Rosoman - Negotino Name in Macedonian: Gradsko - Rosoman - Negotino (rpagcKO - PocoMaH - HeroTHHo) IBA code: MK021 Criteria: A1, A3, B2 Area: 27,692 ha Central coordinates: 21o58'40.95"E, 41o32'29.04"N Altitude: 130-898 m a.s.l. Administrative region(s): Gradsko, Rosoman, Kavadarci, Negotino Site description This is another site in central Macedonia that surrounds parts of the Vardar and Crna Reka Valleys. Starting from the village of Nogaevci to the west it shares the boundary with the Topolka - Babuna -Bregalnica site (MK020) to the pass between the hills of Cucula and Golo Brdo (529 m a.s.l.). Then it turns Table 53: List of triggering and other important bird species in the IBA Gradsko - Rosoman - Negotino Tabela 53: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Gradsko - Rosoman - Negotino Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Aquila heliaca R 2007 6-8 A A1, B2 Coracias garrulus B 2007 20-40 C A1, B2 Neophron percnopterus N 2010 6 ind. B A1 Alectoris graeca R Frequent A3 Oenanthe hispanica B Common A3 Hippolais olivetorum B Rare A3 Lanius nubicus B Rare A3 Emberiza melanocephala B Common A3 Accipiter brevipes B 2007 1-5 C B2 Falco naumanni B 2003 200-250 B B2 Falco biarmicus B 2011 2-3 B B2 Falco vespertinus P 2010 10-50 ind. C A1? Circaetus gallicus B 2007 3-5 B N Buteo rufinus R 2007 2-3 B N Falco peregrinus R 2006 1-2 B N Figure 35: Map of the IBA Gradsko - Rosoman - Negotino with its main features depicted Slika 35: Zemljevid IBA Gradsko - Rosoman - Negotino z glavnimi zna~ilnostmi obmo~ja south to the village of Svekjani, SE to above the village Vodovrati, and SW to above the villages of Gorno Čičevo, Sirkovo and Mrzen Oraovec. From here, the boundary turns east to Trstenik village, crosses the Crna Reka River, then following the road to this village turns SE to the village of Glišic, then turns NE, crossing the Vardar River north of Krivolak village. From here it follows the road and the left banks of the Vardar SE till north of the village of Pepelište, then turns north, passing through Štipsko Ramnište, follows the valley of the Vestinja intermittent stream to Krstata. From here it continues NW to include the peak of Jokuš (300 m a.s.l.), continues west to Kara Odžali, and passes the Slana intermittent stream. After embracing the valley of the Belkamenski Potok, it continues south to Loza and Gjubrišta. Then it turns NW, following the 200 m isohypse till it meets the boundary of the Topolka - Babuna - Bregalnica Rivers site again at Rajnički Rid (392 m a.s.l.) (Figure 35). Parts of the site belong to the Tikveš tectonic depression, intersected by the Vardar and Crna Reka Valleys. The relief is hilly, with abrasive terraces of Table 54: The main CORINE land cover types (Level 3) in the IBA Gradsko - Rosoman - Negotino Tabela 54: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v IBA Gradsko - Rosoman - Negotino Code/ Koda CORINE land cover type/ tip pokrovnosti in rabe tal Coverage/ Pokrovnost (%) 211 Non-irrigated arable land 27.8 242 Complex cultivation patterns 14.4 243 Land principally occupied by agriculture, with significant areas of natural vegetation 5.3 231 Pastures 10.3 221 Vineyards 16.6 321 Natural grasslands 15.7 324 Transitional woodland-shrub 6.8 Other 2.9 fossil lake and recent fluvial terraces. Pliocene lake sediments and recent alluvial deposits are dominant. Figure 36: Characteristic landscape of the IBA Gradsko - Rosoman - Negotino (photo: E. Lisi~anec) Slika 36: Zna~ilna krajina IBA Gradsko - Rosoman - Negotino (foto: E. Lisi~anec) Table 55: The main threats to birds and their importance in the IBA Gradsko - Rosoman - Negotino Tabela 55: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Gradsko - Rosoman - Negotino Code/ Threat/ Koda Dejavnik ogrožanja 110 Use of pesticides 243 Trapping, poisoning, poaching 511 Electricity lines 100 Cultivation 161 Forest planting 730 Military manoeuvres Threat impact/ Most affected species/ Vpliv Najbolj prizadete vrste high F. naumanni, C. garrulus high A. heliaca, A. chrysaetos, B. rufinus high A. heliaca, F. naumanni, C. garrulus medium F. naumanni, C. garrulus medium F. naumanni medium A. heliaca, B. rufinus Species No comprehensive study of the bird fauna of this part of Macedonia has been carried out, although the checklist is quite complete, comprising about 130 species. Most significant species are the Imperial Eagle (6-8 pairs), breeding along the Vardar River, Lesser Kestrel (200-250 pairs), breeding in villages as well as in sand cliffs, which has been rare in the last few decades in Macedonia, Roller (20-40 pairs), Lanner Falcon (2-3 pairs), and a number of Red-footed Falcons during their spring migration. Up to six adult and subadult Egyptian Vultures have been observed in the region, foraging or gathering at predictable food sources, but no recent breeding pair is known. Five species characteristic of the Mediterranean biome regularly breed in good numbers, but with unknown population sizes. Among other important species found below the threshold numbers set, are the Long-legged Buzzard and the Short-toed Eagle (Table 53). Habitats and land use The site is dominated by agricultural land (mostly arable fields, but also many vineyards and some orchards), but at the periphery, dry and sometimes steppe-like pastures are present. The banks of the Vardar are overgrown with riparian vegetation, mostly consisting of poplar and willow trees (Table 54, Figure 36). Threats Intensive agriculture, especially vineyard plantations, still expanding in some parts of the site, have converted large portions of the site into inappropriate habitat for triggering species. Pesticide use both in vineyards and cereal crops is intensive. Some parts of the site have been afforested with allochthonous tree species. Hunting and poaching are present; direct killing of important species, like Imperial and Golden Eagles, has been documented. Along the eastern bank of the Vardar, there is most probably some disturbance present due to military manoeuvres. Mediumtension electricity poles likely cause some mortality in important species (Table 55). Conservation SE parts of the site (Orlovo Brdo) are protected as Nature Monuments (1,981 ha) due to their botanical values. There are no conservation plans for the rest of the territory, nor do any particular bird conservation measures exist. 3.2.17. Lake Mantovo and Kriva Lakavica River Name in English: Lake Mantovo and Kriva Lakavica River Name in Macedonian: Ezero Mantovo i reka Kriva Lakavica (E3epo MaHTOBO u peKa KpuBa .aKaB^a) IBA code: MK022 Criteria: A1, B2 Area: 6,920 ha Central coordinates: 22o18'35.69"E, 41°35'41.38"N Altitude: 350-697 m a.s.l. Administrative region(s): Štip, Konče, Radoviš Figure 37: Map of the IBA Lake Mantovo and Kriva Lakavica River with its main features depicted Slika 37: Zemljevid IBA Jezero Mantovo in reka Kriva Lakavica z glavnimi značilnostmi območja Site description This small site is located in the SE part of Macedonia. Its boundary, starting just east of the hill Pilav Tepe, runs NW around the hill Ruevo Brdo (697 m a.s.l.), then west through the village of Goračino, crosses the Kriva Lakavica River and reaches the isohypse of 400 General information Table 56: List of triggering and other important bird species in the IBA Lake Mantovo and Kriva Lakavica River Tabela 56: Seznam kvalifikacijskih in drugih pomembnih vrst v IBA Jezero Mantovo in reka Kriva Lakavica Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Coracias garrulus B 2007 5-15 C A1 Lanius nubicus B 2007 10-30 C B2 Ciconia nigra B 2008 1 B N Aquila chrysaetos R 2005 1 A N Falco biarmicus B 2008 1 A N Bubo bubo R 2008 2-3 C N Figure 38: Characteristic landscape of the IBA Lake Mantovo and Kriva Lakavica River (photo: M. Velevski) Slika 38: Zna~ilna krajina v IBA Jezero Mantovo in reka Kriva Lakavica (foto: M. Velevski) m. It follows it till east of Leskovica village, where it ascends to 500 m, following it until east of Garvan village. From here it continues south to the village of Zagorci, east to the village of Skoruša and the Radeški Table 57: The main CORINE land cover types (Level 3) in the IBA Lake Mantovo and the Kriva Lakavica River Tabela 57: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Jezero Mantovo in reka Kriva Lakavica Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 211 Non-irrigated arable land 9.8 242 Complex cultivation patterns 18.5 243 Land principally occupied by agriculture, with significant areas of natural vegetation 10.2 231 Pastures 7.7 311 Broad-leaved forest 11.4 324 Transitional woodland-shrub 36.0 512 Water bodies 3.4 Other 3.4 Rid locality, and by following the Radeška Reka rivulet reaches the eastern shore of Lake Mantovo. Then it runs along the lake shore until reaching the Golinite ridge, and continues north to Golema Niva and Samardžica. Here it ascends NW to Golema Čuka (675 m a.s.l.) and then descends east of Pilav Tepe (Figure 37). The site is comprised of the Kriva Lakavica River. In the northern parts dominant are volcanogenic rocks with paleovolcanic relief (volcanic cones) are dominant, while in the southern parts Paleozoic metamorphic rocks prevail. Species The only triggering species for the site are the Roller (5-15 pairs) and the Masked Shrike (10-30 pairs), although several other important species breed in low numbers there: Lanner Falcon, Black Stork, Golden Eagle, Eagle Owl, and possibly Egyptian Vulture (Skorpi'kova et al. 2006). The importance of the lake for waterbirds is unknown, although it is possibly high during migration (Table 56). Habitats and land use The artificial reservoir blends with the landscape, which is composed of volcanic stones and cliffs, Table 58: The main threats to birds and their importance in the IBA Lake Mantovo and Kriva Lakavica River Table 58: Najpomembnejši dejavniki ogrožanja ptic in njihov vpliv v IBA Jezero Mantovo in reka Kriva Lakavica Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 242 Taking from nest (falcons) medium F. biarmicus 243 Trapping, poisoning, poaching medium F. biarmicus 331 Open cast mining medium L. nubicus 701 Water pollution medium C. nigra overgrown with oak scrubland and forms forest stands in places. Part of the site is used for agriculture. The Kriva Lakavica River Valley is densely overgrown with mostly Willow, but also Poplar trees that form well-preserved riparian belts (Table 57, Figure 38). Threats Highest threat comes from the possible expansion of "Damjan" and "Bučim" surface copper mines. Both mines severely pollute the Medenska Reka River, a tributary to the Kriva Lakavica. Nest robbery has been noted. Hunting and poaching probably take place (Table 58). Conservation No specific conservation activities have been planned. 3.2.18. Raec River Valley General information Name in English: Raec River Valley Name in Macedonian: Dolina na reka Raec (öpjjHHa Ha peKa Pae^ IBA code: MK023 Criteria: A1, A3, B2 Area: 19,805 ha Central coordinates: 21o47'41.52"E, 41o23'43.90"N Altitude: 170-1,745 m a.s.l. Administrative region(s): Kavadarci, Prilep, Rosoman Site description The site is situated west of Kavadarci town in southern-central Macedonia. Starting from the village Table 59: List of triggering and other important bird species in the IBA Raec River Valley Tabela 59: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Dolina reke Raec Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2008-2010 2-5 B A1, B2 Alectoris graeca R Frequent A3 Oenanthe hispanica B Common A3 Sylvia cantillans B Common A3 Sitta neumayer R Common A3 Emberiza melanocephala B Common A3 Ciconia nigra B 2007 2-3 B B2 Falco naumanni B 2003 15-25 B B2 Milvus migrans B 2009 0-1 B Circaetus gallicus B 2010 1-2 B N Accipiter brevipes B 2004 1-2 C N Buteo rufinus R 2009 1-2 B N Aquila chrysaetos R 2009 2-3 B N Falco peregrinus R 2010 2-3 B N Bubo bubo R 2008 3-4 B N Figure 39: Map of the IBA Raec River Valley with its main features depicted Slika 39: Zemljevid IBA Dolina reke Raec z glavnimi značilnostmi območja of Debrešte, the boundary runs west to the villages of Fariš and Nikodin, and then turns SW to the villages Krstec and Pletvar. Here, it turns east to the village Table 60: The main CORINE land cover types (Level 3) in the IBA Raec River Valley Tabela 60: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Dolina reke Raec Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 242 Complex cultivation patterns 4.1 243 Land principally occupied by agriculture, with significant areas of natural vegetation 5.7 231 Pastures 6.3 311 Broad-leaved forest 34.9 321 Natural grasslands 10.4 324 Transitional woodland-shrub 34.0 Other 4,6 of Carevik, south to Dren village and east to the village of Galište, then continues north to the villages of Grbovec, Dradnja and Drenovo, before reaching Debrešte again. Smaller part of the site (the lower gorge of the Raec River, known as Drenovo Gorge) was formerly part of the IBA "Crna River Gorge" (MK007, Heath & Evans 2000). North and NW of the Raec River, Mt Babuna with its peak Kozjak (1,745 m a.s.l.) is situated, while south of the river the mountain Dren is located. Geologically, Precambrian metamorphic and magmatic rocks are present in Mt Babuna and Mesozoic formations on Mt Dren. The Drenovo and Fariš Gorges are located in the eastern part of the Raec Valley (Figure 39). Species Some sporadic data on few species have been published for Drenovo Gorge (Kalaber 1970, Danko & Szilard 1971), but no detailed survey exists. Besides significant populations of Egyptian Vultures that declined from 4-5 pairs in 2008 to only two pairs in 2010 (the reasons for this large decline are not known) and Lesser Figure 40: Characteristic landscape of the IBA Raec River Valley (photo: M. Velevski) Slika 40: Zna~ilna krajina IBA Dolina reke Raec (foto: M. Velevski) Kestrels that breed mostly in villages (although a small colony was found in the cliffs as well), the site holds 3-4 pairs of Eagle Owl, 2-3 pairs of Golden Eagle, 2-3 pairs of Black Stork, at least two pairs of Peregrine Falcon, possibly one pair of Black Kite, and several species characteristic of the Mediterranean biome in good numbers (Table 59). Habitats and land use Oak and to a much smaller degree Beech Fagus sylvatica forests are found in the higher parts of the site, but as the altitude decreases forests are replaced by dry pastures and grasslands through different degradation stages. Two small limestone gorges are of highest importance in the site's eastern part, while one large limestone cliff and several smaller silicate cliffs are most important in the western part of the site (Table 60, Figure 40). Threats Private weekend-houses are being built on some key locations. Hunting and poaching probably take place. Livestock numbers have decreased, probably indirectly influencing a number of vultures in the region. Recent forest fires have probably depleted prey base for the birds of prey. Hunting and poaching have also very likely resulted in reduction of prey base, especially for Golden Eagles and Eagle Owls (Table 61). Conservation A small portion of the site (Drenovo Gorge, 9 ha) has been protected. Parts of the site are proposed as "Raec" Emerald Site (MK0000028). Table 61: The main threats to birds and their importance in the IBA Raec River Valley Tabela 61: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Dolina reke Raec Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 960 Interspecific faunal relations high A. chrysaetos, B. bubo 141 Abandonment of pastoral systems medium N. percnopterus, F. naumanni 301 Quarries medium N. percnopterus, B. bubo, B. rufinus 403 Dispersed habitation medium C. nigra 243 Trapping, poisoning, poaching medium N. percnopterus 242 3.2.19. Pelagonia Genetal information Name in English: Pelagonia Name in Macedonian: Pelagonija (ne^aroHHja) IBA code: MK024 Criteria: A1, A4ii, Bliii, B2, B3 Area: 113,584 ha Central coordinates: 21o27'42.20"E, 41o11'59.19"N Altitude: 590-1,538 m a.s.l. Administrative region(s): Bitola, Novaci, Mogila, Prilep, Krivogaštani, Dolneni, Kruševo Site description Situated in southern Macedonia and shared with Greece, this tectonic depression has north-south direction, covering ca. 1,200 km2 in total. Starting west of Prilep town, the boundary runs north to the village of Mažučište, follows the ridge with the peaks Ridot (794 m a.s.l.) and Negrea (988 m a.s.l.), reaches the village Zabrčani, turns NE to the village Dupjacani, then WNW to Desovo, follows the mountain slopes around the village of Brailovo, passes through Slepče village, then west to the village of Kostinci, follows the road WSW to the village Slavej, continues along the road to Rilevo village, and then to the village of Žabjani. Here it turns NW to the village Debrešte (locality Gradište), then south through Slatina and Lozina localities, bypassing the village of Lažani, continues SW to Žitoše village, and then follows the road south to the villages of Lokveni, Godivje and Korenica. The boundary continues west of the village Krivogaštani and east of the village Vrboec, passes through the village of Sveto Mitrani and continues south through Mileševo and Presil villages, till it reaches the Crna Reka River. It embraces the locality Loj in the Crna Reka Valley west of the village Bučin, and from here continues SSW to the village Trnovci, passes east of the village Sveto Todori, reaches the village Ivanjevci and continues SE to Vašarejca. Running parallel with it and then following the road, it reaches western part of the village of Mogila, then follows the channel towards Karamani village and continues south, avoiding the villages of Logovardi and Poeševo, to the village Kravari. From here it follows the road to the south, embraces the village Žabjani, passes through the villages of Porodin and Lažec to the border with Greece. Then it follows the national border towards the east until it reaches southern part of the village Živojno, and turns north through Živojno, Dobroveni and west ofSkočivir. From here it follows the mountain ridge of Selečka Planina and continues through the village of Gnileš. Here it Figure 41: Map of the IBA Pelagonia with its main features depicted Slika 41: Zemljevid IBA Pelagonija z glavnimi zna~ilnostmi obmo~ja turns NW, continues south of the village Paralovo and through the village Baldovenci, when reaching the Tepovska Reka stream. Then it follows the road in NW direction to the south of Biljanik village, embraces the coal mine "Suvodol" and reaches the village Meglenci, from where it runs NW and after ascending to the Selečka Planina again reaches, after passing through the localities Kula (1,103 m a.s.l.), Kalugjer (1,022 m a.s.l.) and Lisičarnik (1,025 m a.s.l.), the main ridge of Golema Gramada Mt (1,050 m a.s.l.). Then it continues north through the peaks of Kozjak (983 m a.s.l.), Liljak (999 m a.s.l.), Bobište (1,266 m a.s.l.), Murgova Niva (1,177 m a.s.l.), Visoko (1,471 m a.s.l.), Skala (1,177 m a.s.l.), Dve Steni (1,473 m a.s.l.) and Konjarnik (1,538 m a.s.l.), where it turns west through Šuti Vrv (1,277 m a.s.l.), descends to the plain again, and passes Prilep at its southern side. The site constitutes the bottom of the Pelagonia Valley and, in the eastern part, the edge (western parts) of Selečka Planina Mt. Geologically, it is dominated Table 62: List of triggering and other important bird species in the IBA Pelagonia Tabela 62: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Pelagonija Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Falco naumanni B 2002 760-850 A A4ii, B1iii, B2 Coracias garrulus B 2002 10-30 C A1, B2 Ciconia ciconia B 2002 220-230 A B2 Aythya nyroca B 2002 10-15 A B2 Burhinus oedicnemus B 2002 10-30 C B2 Lanius minor B 2002 30-100 C B2 Circus pygargus B 2002 60-80 A B3 Falco vespertinus P 2002 50-150 ind. C A1? Pelecanus crispus N 2007 10-30 ind. C N Anas strepera B 2002 2-5 C N Circaetus gallicus B 2008 2-3 B N Buteo rufinus R 2010 3-4 B N Falco biarmicus B 2005 1 A N by Pliocene lake sediments, Precambrian magmatites and metamorphytes in Selečka Planina Mt. The largest river is the Crna Reka in the southern part of the site (Figure 41). Species No thorough information on the site's bird community has been published recently, although numerous Table 63: The main CORINE land cover types (Level 3) in the IBA Pelagonia Tabela 63: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Pelagonija Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 112 Discontinuous urban fabric 1.5 211 Non-irrigated arable land 47.9 212 Permanently irrigated land 21.4 242 Complex cultivation patterns 7.3 243 Land principally occupied by agriculture, with significant areas of natural vegetation 1.2 231 Pastures 12.9 311 Broad-leaved forest 1.5 321 Natural grasslands 0.6 324 Transitional woodland-shrub 4.5 512 Water bodies 0.4 411 Inland marshes 0.1 Other 0.5 data were collected during the Lesser Kestrel and White Stork censuses in 2002 (B. Stumberger & M. Velevski unpubl.). Ample information, however, is available from earlier periods (1940-1970) (e.g. Makatsch 1950, Terrasse & Terrasse 1961A & 1961B, Ganso 1962). The currently drained floodplain of the Crna Reka held numerous breeding colonial waterbirds in the 1930s, the most interesting being up to 100 breeding pairs of Dalmatian Pelican, 60+ pairs of Spoonbill Platalea leucorodia, tens of breeding Glossy Ibises Plegadis falcinellus and ca. 300 pairs of Black Tern Chlidonias niger (Makatsch 1950, Thönen 2006); none of these species breed in the territory of Macedonia at present. In 2002, an important population (largest in the country) of White Stork was confirmed, breeding solitarily or in small colonies of up to 20 pairs (Stumberger & Velevski 2002). Lesser Kestrel population was estimated at 760-850 pairs, entirely confined to villages and man-made structures in the central and northern parts of the plain, but using mountain slopes (especially those of Mt Selečka Planina) for foraging. At least two pairs of Long-legged Buzzards breed on cliffs of these slopes, and one more on a small hill in the plain. Several other species reach the threshold for populations of European importance, including the Montagu's Harrier with the largest breeding population in the country (60-80 pairs). The three fishponds (Bel Kamen and Bukri in the south and Belo Pole in the north) attract non-breeding Dalmatian Pelicans, and are important for the breeding Ferruginous Duck and few pairs of Figure 42: Characteristic landscape of the IBA Pelagonia (photo: B. Stumberger) Slika 42: Zna~ilna krajina IBA Pelagonija (foto: B. Stumberger) Gadwalls (Table 62). Importance of the fishponds for migrating and wintering species is still insufficiently known, although it is presumably high. Habitats and land use The bottom of the Pelagonian depression is used for agricultural purposes, more intensively in the south than in the central and northern parts, where dry and wet meadows and pastures remain. Several poplar tree stands are scattered throughout the landscape, and some remains of the former wetlands can be found. Three fishponds are located within the site. On the eastern edge of the site, the slopes of Mt Selečka are dominated by dry pastures and remains of thermophyllous oak forests, among which silicate cliffs protrude (Table 63, Figure 42). Threats Formerly, the drainage of marshlands of the Crna Reka River caused significant changes in the composition of the site's bird fauna, although presently this process is considered finished. Due to the intensive agriculture in southern parts of the site, use of fertilizers and pesticides is presumably high. Parts of the site are monocultures with low diversity of birds, and their expansion in the plain's northern and central parts might have devastating effects on the populations of the triggering species. Table 64: The main threats to birds and their importance in the IBA Pelagonia Tabela 64: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Pelagonija Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 100 Cultivation high C. ciconia, F. naumanni, C. garrulus, L. minor 110 Use of pesticides high C. ciconia, F naumanni, C. garrulus, L. minor 141 Abandonment of pastoral systems high F. naumanni 511 Electricity lines high C. ciconia, F. naumanni, C. garrulus 803 Infilling of ditches, dykes, ponds, high C. ciconia marshes or pits Livestock numbers have decreased, causing changes in the pastures (overgrowing). Hunting is present, but poaching seems rare. Electrocution causes some mortality, especially in White Storks (Table 64). Conservation The site includes a very small strictly protected area (Lokvi), and parts of the Markovi Kuli Nature Monument. Establishment of protected area has not been formally planned, although most important parts of the site are included in the Emerald Network ("Gorna Pelagonija", MK0000034). Most important for Pelagonian birds are programs preserving and developing different temperate grassland types. Implementation of autochthonous breeds of domestic animals like water buffalo, sheep, shorthorned cattle (Busha) and horses in landscape management is essential to preserve the Pelagonian large scale pasture systems. 3.2.20. Mariovo Name in English: Mariovo Name in Macedonian: Mariovo (MapuoBo) IBA code: MK025 Criteria: A1, A3, B2 Area: 63,272 ha Central coordinates: 21o42'34.4l"E, 4lo09'46.93"N Altitude: 302-1,643 m a.s.l. Administrative region(s): Novaci, Prilep, Kavadarci, Mogila Site description Situated in southern Macedonia, this site includes SW part of the former site "Crna River Gorge" (MK007, Heath & Evans 2000). Starting from the peak Kalusovec (1,446 m a.s.l.) on Selečka Planina Mt SE of Prilep to the south, it shares the boundary with the Pelagonia site (MK024) to the locality Lisičarnik (1,025 m a.s.l.) and the passes at Preslop, Smeč (1,303 m a.s.l.) and Gola Čuka (1,338 m a.s.l.). The boundary continues through the villages of Grumazi and Gnileš, where it again joins the common boundary with Pelagonia running south to the Crna Reka River. Here it turns NE, follows first the river and then the road to the village of Budimirci. Then it follows the Bela Reka River for a short while, turns NE and crosses the hill of Kameni Vrv (1,151 m a.s.l.), the Lešnica and Gradešnička Reka Rivers east of Gradešnica village, turns NW, follows the Porenica River, then runs through Sekulova Tumba (1,057 m Figure 43: Map of the IBA Mariovo with its main features depicted Slika 43: Zemljevid IBA Mariovo z glavnimi zna~ilnostmi obmo~ja a.s.l.), crosses the Potokot River and continues NE to the peak of Perun (1,643 m a.s.l.). From here it follows the mountain ridge north to the peaks of Zelka (1,426 m a.s.l.) and Vragovec (1,107 m a.s.l.), from where it descends to the Crna Reka River again, crosses it below the village of Gudjakovo, continues through this village in NW direction to the peaks of Trite Stragi (1,476 m a.s.l.), Četiri Buki (1,462 m a.s.l.) and Markovi Kuli (1,510 m a.s.l.), turns west to the Golina and Ligurasa passes, and again NW to the peak Studenica (1,664 m a.s.l.). Still following the ridge, the boundary turns SW to the peak Kalusovec again. The site is constituted of the Mariovo Valley, which does not have a flat bottom, as it is broken by the valleys of the Crna Reka River and its tributaries Bela Reka, Buturica, Lisička Reka, etc. It embraces several mountains — Selečka, Nidže, Kozjak and Dren. Pliocene and Miocene lake sediments are found in the site's lowest parts, while the rest is formed by Precambrian metamorphic and magmatic rocks. The Crna Reka Valley includes the remarkable Skočivir Gorge, with General information Table 65: List of triggering and other important bird species in the IBA Mariovo Tabela 65: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Mariovo Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2009 4 A A1, B2 Alectoris graeca R Frequent A3 Oenanthe hispanica B Common A3 Sylvia cantillans B Frequent A3 Sitta neumayer R Abundant A3 Lanius nubicus B Rare A3 Emberiza melanocephala B Common A3 Ciconia nigra B 2009 2-3 B B2 Circaetus gallicus B 2007 8-11 B B2 Buteo rufinus R 2009 8-12 B B2 Aquila chrysaetos R 2009 4-6 B B2 Falco naumanni B 2003 120-150 B B2 Falco biarmicus B 2006 I-2 B B2 Bubo bubo R 2009 5-7 C B2 Monticola saxatilis B 2002-20I0 30-50 C B2 Falco tinnunculus R Common B2? Gyps fulvus R 2010 8-9 A N Accipiter brevipes B 2006 1-3 C N Aquila pennata B 2006 0-1 C Aquila heliaca R 2006 0-1 C Falco peregrinus R 2009 1-3 C N Table 66: The main CORINE land cover types (Level 3) in the IBA Mariovo Tabela 66: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Mariovo Code/ Koda CORINE land cover type/ tip pokrovnosti in rabe tal Coverage/ Pokrovnost (%) 242 Complex cultivation patterns 4.7 231 Pastures 24.6 311 Broad-leaved forest 16.4 321 Natural grasslands 12.9 323 Sclerophyllous vegetation 0.6 324 Transitional woodland-shrub 36.6 Other 4.1 some of the Crna Reka's tributaries forming gorges in the lower sections as well (e.g. Gradešnička Gorge, Buturica Gorge) (Figure 43). Species There are relatively few published data (e.g. GrubaČ 1989, 1997 & 1999) on the bird fauna of Mariovo, although the region has been quite well studied, with about 140 species recorded. It is of great significance for the populations of Griffon (8-9 pairs) and Egyptian Vultures (4 pairs), which are at present the only stable populations in the country. Other birds of prey, especially Golden Eagle (4-6 pairs), Lesser Kestrel (120-150 pairs), Long-legged Buzzard (8-12 pairs), Lanner Falcon (1-2 pairs) and Short-toed Eagle (8-11 pairs), breed here in good numbers, too. The site probably holds populations of some other species that meet B2 thresholds, i.e. Common Kestrel. Species characteristic of the Mediterranean biome include large populations of Black-headed Bunting, Subalpine Warbler, Rock Nuthatch, and a few pairs of Masked Shrike. Furthermore, 2-3 pairs of Black Stork breed here, and possibly a single pair of Imperial Eagle (Table 65). The first record of the Steppe Eagle Aquila nipalensis for Macedonia (one ind. on 15 Jul 2002 near the village of Rapeš, B. Hallmann unpubl.) comes from this region. Habitats and land use The landscape is dominated by large silicate rocks and cliffs in the gorge of Crna Reka River. Formerly Figure 44: Characteristic landscape of the IBA Mariovo (photo: M. Velevski) Slika 44: Zna~ilna krajina IBA Mariovo (foto: M. Velevski) extensively used for agriculture and livestock breeding, this region is now slowly returning to the climax oak forests, while part of the agricultural fields has been converted into dry pastures. The riparian vegetation along the Crna Reka River is composed of poplar and willow. Some pine plantations can also be found (Table 66, Figure 44). Threats Two large hydro-power plants are foreseen to be constructed on the Crna Reka River in the near future, which would submerge part of the cliffs suitable for breeding of Griffon and Egyptian Vultures and increase accessibility to other locations. Stone-mining is widespread, although so far practiced at appropriate Table 67: The main threats to birds and their importance in the IBA Mariovo Tabela 67: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Mariovo Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 141 Abandonment of pastoral systems high G. fulvus, N. percnopterus, A. heliaca 243 Trapping, poisoning, poaching high G. fulvus, N. percnopterus, A. heliaca 960 Interspecific faunal relations high A. chrysaetos, A. heliaca 230 Hunting high G. fulvus, A. graeca 301 Quarries medium A. graeca 410 Industrial or commercial areas medium G. fulvus, N. percnopterus, A. chrysaetos, B. rufinus, A. graeca 530 Improved access to site medium A. graeca 624 Mountaineering, rock climbing, low G. fulvus speleology distances from the area's key localities. Depopulation of villages has been intensive in the past, resulting in decrease in livestock numbers and overgrowing of pastures. Hunting and poaching are common, and poison use, aimed at carnivore control, has been recorded regularly, in turn leading to the death of 19 Griffon Vultures in 2007. Plans exist for the opening of new coal mine, and even for the construction of a nuclear power plant. Hunting causes, besides direct killing of Rock Partridges, disturbance at the breeding sites of Griffon Vultures and decrease in the prey base of other important species (Table 67). Conservation Surprisingly, besides all development plans and exploitation activities in the region, parts of the region are foreseen to be given the status of protected area. Presently, the canyon of Gradešnička Reka River is under protection as a Nature Monument, along with another very small paleontological locality (Manastir). The IBA largely overlaps the proposed Emerald Site (MK0000032). 3.2.21. Lake Tikveš General information Name in English: Lake Tikveš Name in Macedonian: Tikveško Ezero (TuKBemKO E3epo) IBA code: MK026 Criteria: A1, A3, B2 Area: 26,688 ha Central coordinates: 21o57'28.87"E, 41o18'36.30"N Altitude: 260-1,480 m a.s.l. Administrative region(s): Kavadarci, Prilep Site description This is another site in southern Macedonia, located SW of the town of Kavadarci. It occupies the northern part of the former "Crna River Gorge" site (MK007, Heath & Evans 2000). Starting at the artificial Lake Tikveš shore near the island of Gradište on the northern end of the lake, the boundary runs west following the Drenovica River to Dradnja village and leaving part of the lake outside the site, from where it shares the boundary with the Raec River Valley site (MK023), going SW and south to the ridge west of the village of Galište. From here, following the same ridge south, it crosses Lake Tikveš to the influx of the Crna Reka River, reaching the peak of Nedelka (843 m a.s.l.) and turning east at the ridge Varelova Tumba (769 m a.s.l.). Thereupon it continues south, Figure 45: Map of the IBA Lake Tikve{ with its main features depicted Slika 45: Zemljevid IBA Tikve{ko jezero z glavnimi zna~ilnostmi obmo~ja following the rivulet that springs under the ridge of Golem Draguj, passes the saddle and after a short while follows the Došnica River NE to the locality Grkovite Nivi. Here it turns east, avoiding Klinovo village, and continues south to the peak of Ržanovo (1,097 m a.s.l.). Then it follows the ridge of Čatino, turns east and crosses the Blašnica River west of Mrežičko village. From here it continues NE and through the localities Ramnište and Elata, when it reaches the Parnapeš rivulet, following it upstream and east to the road on the Vitačevo plateau. This road, running north, shares the boundary with the Bošavija site (MK027), to the crossroads at Stragovo village. The IBA Lake Tikveš boundary continues north following the same road until it reaches the locality Kozarinov Kamen (in this section, the boundary is shared with the Tikveš Region site, MK013), from where it turns west to the villages of Dabnište and Resava, reaching the shores of Lake Tikveš again. Mt Orlite occupies the western parts, Mt Kožuf Table 68: List of triggering and other important bird species in the IBA Lake Tikveš Tabela 68: Seznam kvalifikacijskih in drugih pomembnih vrst v IBA Tikveško jezero Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2010 3 A A1, B2 Alectoris graeca R 2009 20-50 C A3 Oenanthe hispanica B Common A3 Sylvia cantillans B Abundant A3 Sitta neumayer R Frequent A3 Emberiza melanocephala B Frequent A3 Ciconia nigra B 2010 2-3 B B2 Circaetus gallicus B 2009 5-8 B B2 Buteo rufinus R 2009 4-5 B B2 Aquila chrysaetos R 2009 3-4 B B2 Falco naumanni B 2003 70-100 A B2 Monticola solitarius B 2003-2010 20-50 C B2 Gyps fulvus R 2007-2010 5-9 A N Aquila pomarina B 2010 0-2 C Milvus migrans B 2007 1 A N Accipiter brevipes B 2008 0-2 C Falco peregrinus R 2009 3-4 B N Bubo bubo R 2009 4-8 B N the southern parts and Vitačevo plateau the eastern parts of the site. Geologically, Mesozoic formations are dominant, i.e. Triassic, Jurassic and Cretaceous metamorphic and magmatic rocks with significant presence of Mesozoic carbonates. Vitačevo is composed of volcanic tuffs. The Crna Reka River forms the main gorge, its major tributary being the Blašnica River (Figure 45). Species The area of Lake Tikveš has been well studied, with the total number of observed species reaching 176. The number of vagrant species on the Lake is large (VAsic 2009B), but the carried out winter censuses have shown that it is not of international nor national importance for wintering waterbirds (up to 670 ind. in 2009 and 280 in 2010, Vasic 2009B, Farmahem 2010). However, its surrounding has long been recognized as a place of great importance for the raptors — it has been the last known breeding place of the Lammergeier Gypaetus barbatus in Macedonia (Grubač 1990), breeding until 1984 and the surviving male being present there until 2005-2006. The Griffon Vulture colony decreased from nine to five pairs in the last few years, although still probably numbering around 20 pairs in the late 1990s (B. Grubač unpubl.). Currently, the only three breeding pairs of Egyptian Vulture signify a decrease from 10 pairs in 1991 (B. Grubač unpubl.). Other raptor species include Lesser Kestrel (70-100 pairs), Golden Eagle (3-4 pairs), Short-toed Eagle (5-8 pairs), Long-legged Buzzard (4-5 pairs), Peregrine Falcon and Eagle Owl. Large populations of five species characteristic of the Mediterranean biome are found here. A small colony of Alpine Choughs (2030 pairs) inhabits the highest peaks (Orlite 1,480 m a.s.l.). Other important or rare species include Black Stork, Black Kite and, until 2006, a single individual Table 69: The main CORINE land cover types (Level 3) in the IBA Lake Tikveš Tabela 69: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Tikveško jezero Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 231 Pastures 5.0 311 Broad-leaved forest 45.9 321 Natural grasslands 4.0 323 Sclerophyllous vegetation 9.2 324 Transitional woodland-shrub 22.2 512 Water bodies 3.4 Other 10.2 Figure 46: Characteristic landscape of the IBA Lake Tikveš (photo: M. Velevski) Slika 46: Značilna krajina IBA Tikveško jezero (foto: M. Velevski) of Black Vulture Aegypius monachus, being the last known individual present in the country. Also, two pairs of Lesser-spotted Eagles breed in or in the near surroundings of the site (Table 68). Imperial Eagles are observed outside the breeding season, and a record of Steppe Eagle Aquila nipalensis exists (two ind. on 14 Jun 2004 on the vulture feeding site at Vitačevo, B. Hallmann unpubl.). Habitats and land use The lowest parts of the site embrace Tikveš reservoir, a long and narrow water body between the slopes overgrown with sub-Mediterranean scrub (Greek Juniper Juniperus excelsa, Downy Oak Quercus pubescens, Mock Privet Phyllirea media). In some parts, well preserved remains of Macedonian Oak Quercus trojana forests exist, while in the southern parts, Black Pine Pinus nigra forests are present. Limestone cliffs are scattered throughout the landscape in the valleys of the Crna Reka, Blašnica and Kamenica Rivers, forming a huge complex together with the peaks of Orlite and Galčin in the centre of the site. Some pastures in different stages of succession have remained on the Vitačevo plateau (Table 69, Figure 46). Table 70: The main threats to birds and their importance in the IBA Lake Tikveš Tabela 70: Najpomembnejši dejavniki ogrožanja ptic in njihov vpliv v IBA Tikveško jezero Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 243 Trapping, poisoning, poaching high G. fulvus, N. percnopterus 403 Dispersed habitation high G. fulvus, C. nigra, C. gallicus 141 Abandonment of pastoral systems medium G. fulvus, N. percnopterus 160 General forestry management medium C. nigra, C. gallicus, A. pomarina 511 Electricity lines medium G. fulvus, N. percnopterus, F. naumanni Threats The lake shore is built up by weekend cottages, which are frequently used as bases for illegal fishing and hunting. Intensive forestry activities, including clearcuts, take place. Use of poisonous baits is still common. The Vitačevo plateau is intersected by many power lines, although direct mortality of birds of prey has not been noted (Table 70). Conservation Although parts of the site have been under legal protection as a strict nature reserve since 1997, no management activities have taken place. The new valorization study suggests the site will need to change its protection category into a lower one (i.e. Nature Monument), as it has lost many of its natural assets it used to have. A new management plan was recently prepared by the Ministry of Environment and Physical Planning and UNDP - United Nations Development Programme, but the site does not have a management body. Parts of the IBA are proposed as "Tikvesh" Emerald Site (MK0000006). Supplementary feeding for vultures has been regularly taking place for almost two decades, undertaken by the Aquila Nature Conservation. 3.2.22. Bošavija General information Name in English: Bošavija Name in Macedonian: Bošavija (EomaBHja) IBA code: MK027 Criteria: A1 Area: 9,286 ha Central coordinates: 22o06'53.53"E, 4lo16'16.92"N Altitude: 377-1,280 m a.s.l. Administrative region(s): Kavadarci, Demir Kapija Site description Starting at Stragovo village, the boundary of the site runs SW following the village road, until reaching the main road on the Vitačevo plateau (common border with the Tikveš Region site, MK013). It follows the road southwards (common border with the site Lake Tikveš, MK026) to the Čaškite locality, where it turns eastwards and runs through Prodanovec, crosses the Lisač River, the peak of Kumanova Glava (1,066 m a.s.l.) and the Bošava River, and by following the ravine north ofVasiljova Padina reaches the isohypse of 1,100 m at the Popranca locality. Then it follows the same isohypse to the Madžarsko Borče locality, crossing it and descending into the valley of the Dobošnica River. From here it follows the river downstream and north to the Dina locality, where it ascends to the Jurkov Rid locality and follows the ridge Gatenovo north to its peak (990 m a.s.l.). Here it turns west, descends through a ravine to the Bohulska Reka, following it to its confluence with the Bošava River. Then it turns SW following the Bošava to Krnjevo village, from where it follows the ridge NW to the village of Stragovo (Figure 47). The valley of the Bošava River is dominant at the site, with the Vitačevo plateau in the western parts and slopes of Mt Kožuf in the south and east. Denudation forms are characteristic of the site, with different sand pillars and sand cliffs. Species This site was formerly part of the larger "Kožuf Mt and Bošava River" site (MK009, Heath & Evans 2000), but the boundaries have been changed a great deal, as the importance of the rest of this site has not been confirmed with the surveys carried out in 2003 and 2004. The site has been relatively poorly studied; its importance was identified solely due to the presence of three breeding pairs of Egyptian Vultures in 2007 and at least three more before 1990 (B. Grubač Table 71: List of triggering and other important bird species in the IBA Bo{avija Tabela 71: Seznam kvalifikacijskih in drugih pomembnih ptic IBA Bo{avija Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Neophron percnopterus B 2007-2010 1-3 A A1 Circaetus gallicus B 2007 2-3 B N Buteo rufinus R 2005 2 B N Aquila chrysaetos R 2010 1 B N Aquila pomarina B 2010 0-1 B Figure 47: Map of the IBA Bo{avija with its main features depicted Slika 47: Zemljevid IBA Bo{avija z glavnimi zna~ilnostmi obmo~ja unpubl). However, two of the pairs have been lost in the 2007-2008 period. Also, two pairs of Long-legged Buzzard and single pairs of Golden Eagle, Short-toed Table 72: The main CORINE land cover types (Level 3) in the IBA Bo{avija Tabela 72: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Bo{avija Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 211 Non-irrigated arable land 5.0 231 Pastures 10.9 242 Complex cultivation patterns 4.5 243 Land principally occupied by agriculture, with significant areas of natural vegetation 10.4 311 Broad-leaved forest 36.0 321 Natural grasslands 10.8 324 Transitional woodland-shrub 22.4 Eagle and possibly Lesser Spotted Eagle have been confirmed breeding there (Table 71). Habitats and land use Oak and Beech Fagus sylvatica forests are dominant in the SE part of the site, while dry pastures prevail on the Vitačevo plateau. Agriculture is mosaic, mostly with small vineyards and gardens. Small sand cliffs are found along the Bošava River, forming suitable places for breeding of raptors (Table 72, Figure 48). Threats Poisoning in the wider surroundings, outside the IBA, has caused the loss of one, possibly both Egyptian Vulture pairs breeding at this site. Forestry activities impact the insufficiently studied oak and Beech forests, and hunting, possibly even poaching, takes place. New dangerous electricity poles have been recently erected. The area is being increasingly urbanized with weekend cottages, although permanent population is decreasing (Table 73). Figure 48: Characteristic landscape of the IBA Bošavija (photo: M. Velevski) Slika 48: Značilna krajina IBA Bošavija (foto: M. Velevski) Table 73: The main threats to birds and their importance in the IBA Bošavija Tabela 73: Najpomembnejši dejavniki ogrožanja ptic in njihov vpliv v IBA Bošavija Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 141 Abandonment of pastoral systems high N. percnopterus 243 Trapping, poisoning, poaching high N. percnopterus, A. chrysaetos 160 General forestry management medium A. pomarina 511 Electricity lines medium N. percnopterus 400 Urbanised areas, human habitation medium A. chrysaetos Conservation A small protected area (Konopište) aimed at conserving the geomorphologic structures was designated. No active conservation measures are ongoing, and the rest of the site is not foreseen for any form of legal protection. 3.2.23. Kočani Rice Fields Name in English: Kočani Rice Fields Name in Macedonian: Kočanski orizovi polinja (KonaHCKH 0PH30BH nojjH^a) IBA code: MK028 Criteria: B2 Area: 11,192 ha Central coordinates: 22o19'39.76"E, 41o52'38.18"N Altitude: 280-400 m a.s.l. Administrative region(s): Češinovo-Obleševo, Karbinci, Kočani, Probištip, Vinica, Zrnovci General information Figure 49: Map of the IBA Ko~ani Rice Fields with its main features depicted Slika 49: Zemljevid IBA Ko~anska riževa polja z glavnimi zna~ilnostmi obmo~ja Site description Starting from the Bregalnica River west of Karbinci village, the site's boundary runs north for a short while following the railway, and then reaches the irrigation channel under the Rid locality (443 m a.s.l.). From here the site shares the boundary first with the IBA Ovče Pole (MK019) and then with the IBA Zletovska River Valley (MK012) right to the east of Sokolarci village. From here it continues eastwards to the village of Banja, follows the irrigation channel and via Preslop locality (393 m a.s.l.) reaches the village of Trkanje. Then it continues east along the channel to the stream of Belski Dol, follows it southwards to the Kočanska Reka River, and from here runs eastwards, first following the river, and then the road south of Kočani town, until reaching the Kočanska Reka again. From here it continues eastwards, following the local road to Toplički Rid, where it turns south and crosses Table 74: List of triggering and other important bird species in the IBA Ko~ani Rice Fields Tabela 74: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Ko~anska riževa polja Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Ciconia ciconia B 2011 150-180 A B2 Ardea cinerea B 2009 50-70 B N Egretta garzetta B 2009 10-30 C N Nycticorax nycticorax B 2009 10-30 C N Figure 50: Characteristic landscape of the IBA Kočani Rice Fields (photo: G. Camlik) Slika 50: Značilna krajina IBA Kočanska riževa polja (foto: G. Čaml(k) Table 75: The main CORINE land cover types (Level 3) in the IBA Kočani rice fields Tabela 75: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Kočanska riževa polja Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 211 Non-irrigated arable land 44.2 213 Rice fields 36.2 242 Complex cultivation patterns 10.3 243 Land principally occupied by 6.1 agriculture, with significant areas of natural vegetation 324 Transitional woodland-shrub 34.0 Other 3.2 the Bregalnica River. Then it continues parallel to the river in SW and W directions, along small dirt roads or the riverbed, until reaching the starting point west of Karbinci village again. The plain is a tectonic depression, with soils of alluvial origin, while on its northern edge delluvial soils are also found. Main rivers are the Bregalnica and its right tributary Zletovska Reka River (Figure 49). Species The bird fauna of this IBA is virtually unknown, without any published information. Very large numbers ofWhite Stork pairs (150-180) breed in the villages of this region (Heckenroth & Heins in prep.), using its rice fields for foraging. Its breeding density is substantially larger than at Pelagonia Table 76: The main threats to birds and their importance in the IBA Kočani Rice Fields Tabela 76: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Kočanska riževa polja Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 110 Use of pesticides high C. ciconia, E. garzetta, N. nycticorax, A. cinerea 101 Modification of cultivation practices medium C. ciconia, E. garzetta, N. nycticorax, A. cinerea 511 Electricity lines medium C. ciconia (the largest population in Macedonia), making the site of special importance for the conservation of the species. This site also holds the only known mixed colony of herons in Macedonia, consisting of Grey Herons, Night Herons and Little Egrets - for the latter, this is at present the only known breeding locality in Macedonia. Two more Grey Heron colonies are known within this site (Table 74). The importance of rice fields for breeding and migrating waterbirds is unknown, although presumably high. Habitats and land use The extensive rice fields give this site its characteristic image. They are usually flooded in May, and the water is retained there till August. Some of them periodically turn into other arable plots of land, thus creating mosaic landscape. Small patches of reedbeds are also found. The riparian forests with poplar and willow along the Bregalnica River are preserved in a narrow belt, presumably maintaining high biodiversity value (Table 75, Figure 50). Threats The threats are not sufficiently documented. Pesticide use is common during rice cultivation. Also, the number of ponds dried for the purpose of growing other crops (notably maize) seems to have been on increase in the last few years. Dangerous power poles are common in the region, very likely causing significant mortality of the storks (Table 76). Conservation No active conservation measures are ongoing, and the site is not foreseen for any legal protection. 3.2.23. Lower Vardar General information Name in English: Lower Vardar Name in Macedonian: Dolen tek na reka Vardar (gogeH TeK Ha peKa Bapgap) IBA code: MK029 Criteria: B2 Area: 5,357 ha Central coordinates: 22o31'58.42"E, 41o11'28.71"N Altitude: 40-192 m a.s.l. Administrative region(s): Bogdanci, Gevgelija, Valandovo Site description Starting from the right bank of the Vardar River along the Macedonian - Greek border, the site boundary 2F7TE SS"3CfE H"33t »'WE Figure 51: Map of the IBA Lower Vardar with its main features depicted Slika 51: Zemljevid IBA Spodnji Vardar z glavnimi zna~ilnostmi obmo~ja follows the state border eastwards to l the Selemilska Reka stream, from where it turns NW and via Mala Čuka (196 m a.s.l.) descends towards the village of Stojakovo, including it into the site, and along a dirt road continues NW to include the village of Gjavato. From there it continues north, passing close to the left bank of the Vardar, leaving the greenhouses at Grčište village outside the site. Then it continues north along the local road till it reaches the E-75 Demir Kapija-Gevgelija motorway, passes through the Šopka and Lagovo localities until reaching the Anska Reka River, follows it east to the motorway, and then runs along it north to just south of Udovo village. The boundary crosses the Vardar at its confluence with the Selište stream and turns south towards the railway station at Miravci village, passes through the Vrežot locality (66 m a.s.l.) along a dirt road and close to the Vardar River, continues south, crosses the Petruška Reka and reaches the railway. Then it follows the railway to the east of Negorci village, when it turns eastwards and Figure 52: Characteristic landscape of the IBA Lower Vardar (photo: M. Velevski) Slika 52: Zna~ilna krajina IBA Spodnji Vardar (foto: M. Velevski) Table 77: List of triggering and other important bird species in the IBA Lower Vardar Tabela 77: Seznam kvalifikacijskih in drugih pomembnih vrst ptic v IBA Spodnji Vardar Species/ Season/ Year/ Population/ Acc./ Criteria/ Vrsta Sezona Leto Populacija Zan. Kriteriji Ciconia ciconia B 2OII 50-60 A B2 Sternula albifrons B 2OO9 I5-3O B B2 Riparia riparia B 2OIO 8oO-I,2OO B B2 Sterna hirundo B 2009 15-30 B N Table 78: The main CORINE land cover types (Level 3) in the IBA Lower Vardar Tabela 78: Glavni tipi pokrovnosti in rabe tal (po CORINE land cover, 3. nivo) v iBa Spodnji Vardar Code/ CORINE land cover type/ Coverage/ Koda tip pokrovnosti in rabe tal Pokrovnost (%) 211 Non-irrigated arable land 15.1 242 Complex cultivation patterns 46.7 243 Land principally occupied by agriculture, with significant areas of natural vegetation 4.3 231 Pastures 16.2 221 Vineyards 5.9 511 Water courses 5.7 Other 6.0 approaches the Vardar again. Close to its right bank, it reaches the state border again (Figure 51). The Vardar riverbed between Udovo and Gevgelija is morphologically characterized by the monochannel's transition into a braided river type. This is the area with best-preserved natural river dynamics in Macedonia. The entire site is part of the Gevgelija-Valandovo valley, of tectonic origin. Alluvial deposits are found on both sides of the Vardar, but are most characteristic in western parts of the valley (the Miravci field). Aeolian sands are found in the vicinity of Gjavato village. Species The segment of the Vardar River near Gevgelija is important for a mixed colony of Common Sterna hirundo and Little Terns Sternula albifrons with at least 15 pairs of both species (Skorpi'kova et al. 2009A) breeding on large Table 79: The main threats to birds and their importance in the IBA Lower Vardar Table 79: Najpomembnej{i dejavniki ogrožanja ptic in njihov vpliv v IBA Spodnji Vardar Code/ Threat/ Threat impact/ Most affected species/ Koda Dejavnik ogrožanja Vpliv Najbolj prizadete vrste 810 Drainage high C. ciconia 300 Sand and gravel extraction high S. albifrons, S. hirundo, R. riparia 410 Industrial or commercial areas high C. ciconia, S. albifrons, S. hirundo, R. riparia 511 Electricity lines medium C. ciconia gravel islets in the riverbed. Furthermore, at least two colonies (one of which is very large with > 800 pairs) of Sand Martins Riparia riparia were found (M. Velevski unpubl.). Truly spectacular passerine congregations during the migration period were also recorded (e.g. up to 2 million Barn Swallows Hirundo rustica in autumn along the Vardar River in September 1990, B. štumberger unpubl.). Migration of soaring birds (raptors, storks) has not been studied, but is expected to be important, probably as a bottleneck site. Nearly 10% of the country's White Stork population breed within the IBA Lower Vardar. The large stork colonies in Stojakovo and Bogorodica villages held 28 and 21 breeding pairs in 2010, respectively (Heckenroth & Heins in prep.) (Table 77). Habitat and land use Remains of alluvial forests (e.g. willows, Oriental Plain Platanus orientalis), numerous gravel bars and sand river banks, reedbeds, and predominant mosaic agriculture in the lowlands on river deposits are the main features of this floodplain area. Tamarisk belts and shrublands are also well-preserved. Small hills are dominated by pastures, while some areas have been afforested with allochthonous tree species (Table 78, Figure 52). Threats A windfarm near the village of Miravci has already been approved. Gravel extraction takes place at several locations along the Vardar River. A large field near Bogorodica village was drained by channels. The existing dangerous power poles very likely cause mortalities in the White Stork population. The planned construction of a dam on the Vardar River just north of the site (at the village of Gradec) will probably change the entire water-regime downstream, altering sandbanks, gravel deposition and riparian vegetation. A pipeline is planned to pass through this region, and appropriate mitigation measures to conserve the floodplain will be needed (Table 79). Conservation No active conservation measures are ongoing, and the site is not foreseen for any legal protection. 4. Discussion Three of the identified IBAs occupy the highest parts of the large mountain massifs, while three other IBAs embrace the large natural lakes. The rest are mostly located in the lower mountainous or hilly and especially lowland parts of the country, including breeding areas of species of global conservation concern. The percentage of territory covered by the IBAs in the country is relatively high, although less than Croatia with 40% of the land territory (Radovic et al. 2005) and Spain with ca. 32%, almost identical to Slovenia with 27% (Denac et al. 2011), Greece with 26% (Heath & Evans 2000), and just slightly above Bulgaria with 23%, (Kostadinova & Gramatikov 2007). The fact that Macedonia has a much lower number of sites compared to these countries (Table 80), indicates their relatively large size. Indeed, almost the entire Pčinja - Vardar Valley, starting from the Serbian border in the north to Demir Kapija to the south, adjoined by Mariovo and Pelagonia, may be actually considered as one territory of clear importance for the conservation of species of the global conservation concern. This is largely due to the fact that IBA identification was possible primarily on the basis of occurrence of large raptors due to the precise quantitative data. As many of them have large home-ranges and some pairs even frequently change their breeding sites in consecutive breeding seasons, particularly the Imperial Eagle, inclusion of large areas in the network is justified. Compared to the other IBAs designated for the birds of prey in the Southern European region, the number of breeding pairs per area unit in Macedonia is well within the range. This IBA network includes significant portion of the national population of the species of global conservation concern. Specifically, about 80—90% of Table 80: Comparison of number of IBAs and their total coverage among countries of Southern Europe and its surroundings Tabela 80: Primerjava med {tevili IBA-jev v državah južne Evrope z okolico in skupna povr{ina IBA-jev v posameznih državah Country/ Country size/ Total IBA coverage/ Skupna površina IBA-jev (km2) Percentage of territory under IBA/ Total no. of IBAs/ Država Velikost države (km2) Odstotek ozemlja v okviru IBA (%) Skupno št. IBA-jev Albania 28,750 903 3 15 Armenia 29,800 1,820 6 5 Azerbaijan 86,600 6,161 7 52 Bosnia 51,130 68 < 1 3 Bulgaria 110,994 26,021 23 114 Croatia 56,540 22,654* 40* 40 Cyprus 9,250 1,305 14 16 France 551,600 47,248 9 277 Greece 132,000 34,332 26 196 Hungary 93,032 14,662 16 43 Italy 301,302 46,270 15 192 Macedonia 25,713 6,907 27 24 Moldova 33,700 509 2 12 Portugal 89,000 9,421 11 34 Romania 237,500 6,557 3 44 Serbia 88,361 12,596 14 35 Slovenia 20,272 5,538 27 35 Spain 492,463 157,689 32 391 Turkey 779,452 29,978 4 97 Ukraine 603,700 20,323 3 102 Croatia after Radovic et al. (2005), Bulgaria after Kostadinova & Gramatikov (2007), Serbia after Puzovic et al. (2009), and Slovenia after Denac et al. (2011), all other countries after Heath & Evans (2000) * only land IBAs (marine sites excluded) the national Imperial Eagle breeding population, all but one known pair (95% of the national population) of Egyptian Vultures, all known possibly breeding pairs of the Saker Falcon, all non-breeding and wintering individuals of Dalmatian Pelican, 40-75% of the Ferruginous Duck population and at least 40-50% of the Roller population are included in the IBA network. With regard to the species of European importance, 80-100% of all Lesser Kestrel pairs, 50-60% of the Long-legged Buzzard, ca. 50% of the Lanner Falcon breeding population, 45-55% of the Short-toed Eagle, 40-50% of the Golden Eagle, 3050% of the Eagle Owl, 35-45% of the Black Stork, 25-50% of the Peregrine Falcon and ca. 20-25% of the Levant Sparrowhawk populations of are included. Furthermore, all known breeding pairs and main foraging areas of the Griffon Vultures are also covered by the network. The network is also representative of the species characteristic of the Eurasian high-montane biome and the Mediterranean biome (except for the Sardinian Warbles Sylvia melanocephala) (Appendix 5). A large gap exists in the knowledge regarding the population sizes of many species, especially passerines, and priority for further research should be placed on the species that presumably meet the 0.5% threshold of the European populations, for which there is not enough information available at the moment to support site-based conservation approach (Appendix 1). These are mainly species occupying a variety of habitats and widely distributed throughout the country. Also, for a few species for which site-based conservation approach is considered suitable, lack of quantitative data prevented us from identifying the best sites. Of highest importance are efforts to precisely estimate the breeding population of the globally Near Threatened Semicollared Flycatcher, as breeding records exists from the northernmost (Skorpi'kova et al. 2009B) to the southernmost (Hölzinger 1987) parts of the country. There are still gaps in knowledge on the distribution and population estimates for several important species, and improving of this situation may result in identification of additional IBAs. The Sardinian Warbler (triggering species under the A3 criterion as a part of the Mediterranean biome species assemblage) is evidently underrepresented in the network, although no less than eight sites were identified that hold significant numbers of different species characteristic of the Mediterranean biome. This species, opposite to other species of this assemblage, is found in Macedonia almost exclusively in the pseudomaquis in the southernmost part of the country (roughly the triangle between Demir Kapija, Gevgelija and Lake Dojran), and some part of the population may be included in the Demir Kapija Gorge site (MK008), although no firm data exist. However, further survey of this region aimed at this species is needed to delineate additional IBA, which would ideally also include potentially important populations of some other more or less underrepresented species, e.g. Levant Sparrowhawk, Booted Eagle, Lesser Spotted Eagle and some other Mediterranean species. Parts of the Skopje Valley might hold important White Stork numbers (the population has increased since the work published by Micevski et al. 1992), and also possibly important population of the Roller, as at some places along the Vardar River its density of 1.5 pairs/km2 has been noted (M. Velevski unpubl.). The surroundings of Monospitovo Marsh near Strumica also hold important population of White Stork (ca. 60 pairs, Heckenroth & Heins in prep), but at present no other species that might support IBA identification in this area are known. Some of the mountains in western Macedonia, notably Mt Stogovo, may also meet A3 criterion for the species characteristic of the Eurasian high-montane biome. So far, only the Alpine Chough and the Snow Finch have been recorded, although the presence of Wallcreeper and Alpine Accentor is very likely. However, if relative abundance or population sizes are proved to be lower than at the other three sites already identified, we consider identification of additional IBA for this species assemblage not justified. The Matka Canyon near Skopje holds one pair of Egyptian Vultures and several other species characteristic of the Mediterranean biome (A3 criterion), while one species, the Eagle Owl, possibly meets B2 criterion, even though the site has not been proposed as an IBA (Velevski 2008). Abandonment of pastoral system, resulting in decrease of the livestock numbers (overview in Velevski et al. 2003), and overgrowing of the pastures have been identified as one of the most serious threats at 11 sites. It most negatively impacts the vultures (most notably Griffon Vulture at the national level) and other facultative necrophagous species such as the Imperial and Golden Eagles. Habitat loss due to overgrowing of the pastures negatively affects species that use this habitat for foraging (notably Lesser Kestrel in the lowlands and Alpine Chough in the mountains) or breeding (Stone Curlew). Equally important threat, also with estimated high impact at 11 sites, are direct losses from poaching and poisoning resulting in dramatic decrease in the number of vultures and, very likely, Imperial Eagles. Interspecific faunal relationships, particularly reduction of the natural prey base due to habitat changes, overhunting and poaching (notably the European Hare Lepus europeus, Roe Deer Capreolus capreolus and Alpine Chamois Rupicapra rupicapra), but since recently also overharvesting of tortoises (Testudo hermanni and T. graeca) are likely having a negative impact on raptors and possibly scavengers that are exposed to the additional risk of secondary lead poisoning. About 21% of the identified IBAs overlap the national protected area network (Melovski et al. in prep). Notably underrepresented are regions in the lower parts of the country, which means that the populations of Imperial Eagle, Lesser Kestrel, Roller and to some degree Egyptian Vulture inhabit the areas outside the boundaries of the existing protected areas. The situation is somewhat better with the mountainous IBAs and particularly the natural lakes. However, management measures oriented towards bird conservation are rarely a practice. High coverage of agricultural areas on the IBAs (totalling almost half of the entire surface area) suggests that promotion of new protected areas is likely to be difficult, and conservation measures will be highly dependent on suitable implementation of agri-environmental schemes in the country. Acknowledgements: Most of the data on the birds of prey used in this work were collected in the 20032010 period, during field work carried out within the framework of the Vulture Conservation Project in Macedonia, financed by the Frankfurt Zoological Society (FZS) (Germany), Black Vulture Conservation Foundation (BVCF) and Vulture Conservation Foundation (VCF). Significant contribution during the field work was provided by Bobi Delov, Mladen Pop Trajkov, Jovan Andevski, Elizabeta Dimitrovska, Marjan Manoilov and Kostadin Kočov. Vlasta Skorpikova and Vaclav Prašek (Czech Ornithological Society) also made available their field data from Macedonia, some of them having been used for more precise estimation of the populations of certain species. Hartmut Heckenroth and Jens-Uwe Heins (The Stork Foundation) kindly made available their unpublished data from the White Stork census. Macedonian Ecological Society (MES) allocated significant resources to support the work on the data collection, analyses and presentation. Aleksandar Sarov (MES) provided valuable help with the GIS software. Biology Students' Research Society made possible for the first author surveys in several mountains in Macedonia. Dr Dragan Kolčakovski offered assistance during description of the geology, geomorphology and hydrography of the sites. Ministry of Environment and Physical Planning of Republic of Macedonia made available the Emerald database to the MES, from where the threat codes and digital boundaries of the Emerald sites became available. Dr Ian Burfield (BirdLife International) made available the original fact sheets (with boundaries) of the first pan-European IBA inventory that were used as a foundation for the identification of the new IBAs, provided valuable guidance and suggestions during the entire process of identification of the IBAs. Wetlands International made available to the MES all historical data for the mid-winter counts in Macedonia. The Ministry of Agriculture, Nature Management and Fisheries of the Netherlands supported the Imperial Eagle work of Ben Hallmann. Club 300 Foundation, Sweden, supported FWFF - Bulgaria and "Aquila" NCA work on the Lesser Kestrel and Imperial Eagle, while the Fund for Wild Flora and Fauna - Bulgaria supported the Imperial Eagle, Lesser Kestrel and vultures censuses in the 2000-2003 period. Parts of the expenses for the fieldwork, carried out by the MES during 2010 and 2011, and the time dedicated to this work by the first author were made possible within the project "Wings Across the Balkans: Preparing countries in the Western Balkans for implementing the EU Birds Directive", led by BirdLife International (European Division) and financed by the assistance of the European Union, from the pre-accession funds - Instrument of Pre-accession (IPA), as part of the "Partner activities" programme IPA Civil Society Facility. Earlier draft of the manuscript was kindly improved by Vlasta Skorpikova and Dr Slavčo Hristovski. Photographs were kindly provided by: Žarko Brajanoski, Gašpar Čamlfk, Dr Slavčo Hristovski, Dr Ljupco Melovski and Borut Rubinic. 5. Povzetek (SI) / Pe3HMe (MK) Opredeljevanje Mednarodno pomembnih območij za ptice (IBA) je pobuda, ki jo organizacija BirdLife International izvaja na svetovni ravni, njen glavni namen pa je zavarovati mrežo območij, ki so še posebej pomembna za ohranitev ptic. S spremenjenim naravovarstvenim statusom nekaterih ptic in z naraščajočim številom podatkov o razširjenosti in velikosti ptičjih populacij v Makedoniji na splošno je bila potrebna temeljita revizija omrežja IBA za posodobitev popisov, objavljenih v letih 1989 in 2000. Glede na dejstvo, da je ptičja favna Republike Makedonije med najslabše poznanimi v Evropi in še vedno ni na voljo podatkov o mnogih pticah, predvsem pevcih, je popis slonel predvsem na nekaterih ogroženih ali redkih ujedah in še nekaterih večjih pticah, značilnih za makedonsko krajino. Uporabljeni podatki so bili zbrani v obdobju različnih poglobljenih študij in projektov, opravljenih po letu 2000. Od 314 vrst, doslej zabeleženih v Makedoniji, 114 redno pojavljajočih se vrst trenutno obravnavamo kot vrste z neugodnim varstvenim statusom v Evropi, 84 od katerih gnezdi ali domnevno gnezdi v Makedoniji. Za izbor globalno (kriterij A) in evropsko pomembnih (kriterij B) IBA-jev je bilo uporabljenih več kriterijev, ki jih je razvil BirdLife International, pri čemer so bile upoštevane vrste globalne varstvene pozornosti (A1), vrste, strogo vezane ne različne biome (A3), pomembne zgostitve ptic (A4, B1), vrste z neugodnim varstvenim statusom (B2) in vrste, koncentrirane v Evropi (B3). Vrste globalne varstvene pozornosti, uporabljene za določitev območij, vključujejo egiptovskega jastreba Neophron percnopterus, ki je glede na najnovejši Rdeči seznam ogroženih vrst (kategorizacija IUCN -Svetovne zveze za varstvo narave) ogrožen (mednarodna oznaka EN) na svetovni ravni, kodrastega pelikana Pelecanus crispus in kraljevega orla Aquila heliaca (oba ranljiva - VU) ter zlatovranko Coracias garrulus in balkanskega muharja Ficedula semitorquata (oba blizu ogroženosti - NT). Poleg tega so bile v Makedoniji zabeležene skupine vrst, za katere je značilno, da se pojavljajo večinoma ali v celoti znotraj evrazijskega visokogorskega ali mediteranskega bioma. Pomembne zgostitve negnezdečih vodnih ptic z najmanj 1 % globalnih ali biogeografskih populacij posameznih vrst se pojavljajo na vseh treh velikih makedonskih jezerih, nekatere izmed njih (kot na primer kodrasti pelikan in tatarska žvižgavka Netta rufina) celo v zelo velikem številu, tako da presegajo 1-odstotno raven za več kot desetkrat. Za izbor evropsko pomembnih območij je bilo skupaj uporabljenih 25 vrst, ki se tu redno pojavljajo v gnezditveni sezoni in za katere je območno varstvo v Makedoniji ustrezno. Meje posameznih območij so bile zarisane glede na izrazite fizične značilnosti območja ali izohipse, da so lahko zaobjele gnezdišča in prehranjevališča kvalifikacijskih vrst, kar zadeva kraljevega orla in egiptovskega jastreba, pa tudi njuna nekdanja gnezdišča do leta 1991, pri čemer so bila upoštevane habitatne zahteve ptic, raba tal in različne upravljalske potrebe. Seznam IBA-jev, ki je nastal na tej osnovi, vsebuje 24 območij, ki pokrivajo 6.907 km2 ali 26,9 % celotnega makedonskega ozemlja: (1) Šar Planina, (2) Povodje reke Radike, (3) Ohridsko jezero, (4) Prespansko jezero, (5) Soteska Demir Kapija, (6) Dojransko jezero, (7) Dolina Zletovske reke, (8) Tikveško okrožje, (9) Reke Pčinja - Petrošnica - Kriva reka, (10) Preod - Gjugjance, (11) Osogovsko gorovje, (12) Gora Jakupica, (13) Soteska Taor, (14) Ovče Pole, (15) Reke Topolka - Babuna - Bregalnica, (16) Gradsko - Rosoman - Negotino, (17) Jezero Mantovo in reka Kriva Lakavica, (18) Dolina reke Raec, (19) Pelagonija, (20) Mariovo, (21) Tikveško jezero, (22) Bošavija, (23) Kočanska riževa polja, in (24) Spodnji Vardar. Z izjemo treh območij, ki pokrivajo najvišje vrhove velikih gorskih masivov v SZ in osrednjih delih Makedonije, kot tudi Ohridskega in Prespansko jezera so območja koncentrirana predvsem v osrednjih hribovskih in nižinskih delih Makedonije in zaobjemajo gnezditvena območja vrst globalne varstvene pozornosti. Odstotek ozemlja, ki ga pokrivajo IBA-ji v Makedoniji, je razmeroma visok v primerjavi s celotnim evropskim povprečjem, vendar primerljiv z več državami v JV delu Evrope. Velikost posameznih IBA-jev je med 25 km2 (Soteska Taor) in 1.136 km2 (Pelagonija), število kvalifikacijskih vrst na območje pa med ena (Bošavija, Kočanska riževa polja) in 17 (Reke Pčinja - Petrošnica - Kriva reka). 22 območij ustreza nekaterim kriterijem za globalno pomembne IBA-je - tri območja (Ohridsko, Prespansko in Dojransko jezero) kriteriju A4, v osmih gnezdijo pomembne populacije vrst, značilnih za mediteranski biom, medtem ko na treh območjih prebivajo pomembne populacije vrst, značilnih za evrazijski visokogorski biom. Vrste globalne varstvene pozornosti se pojavljajo v različnem številu območij, in sicer: egiptovski jastreb v trinajstih, kraljevi orel v sedmih, kodrasti pelikan in sokol plenilec Falco cherrug v dveh, kostanjevka Aythya nyroca v treh, zlatovranka v desetih, rdečenoga postovka Falco vespertinus v treh in balkanski muhar v enem. Posamezne kvalifikacijske vrste za evropsko pomembna območja so zastopane v 2-15 območjih. Omrežje IBA-jev vključuje 80-100 % nacionalnih populacij globalno ogroženih vrst, medtem ko se zastopanost drugih vrst giblje med 5 in 100 %, vendar prek 40 % za veliko večino vrst. Opuščanje tradicionalnega pastirstva, ki se kaže v zmanjševanju živinskih čred in posledično zaraščanju ter lov s pastmi, zastrupljanje in divji lov sta med najpomembnejšimi dejavniki ogrožanja kvalifikacijskih vrst, še posebno za egiptovskega jastreba in kraljevega orla, saj je bil njun vpliv opredeljen kot velik na nič manj kot enajstih območjih. Nacionalna pravna zaščita območij je vse prej kot popolna, saj je bodisi samo delna ali z neustreznimi varstvenimi ukrepi, ali pa v mnogih območjih kakršne koli pravne zaščite sploh ni. Glede na dejstvo, da se samo 21 % zavarovanih območij prekriva z IBA-ji, je obstoječi sistem torej neustrezen za varovanje večine prednostnih vrst. To še posebno velja za območja v nižje ležečih delih države z največjim številom vrst globalne varstvene pozornosti. *** HgeHTH(^HKa^HjaTa Ha 3Ha^ajHHTe nogpa^ja 3a ^TH^H (3nn) (Important Bird Areas, IBAs) e HHH^HjaTHBa cnpoBegyBaHa og BirdLife International Ha rjioöajHo hhbo, co ga ce 3amTHTH Mpe^a Ha nogpa^ja koh ce og ocoöeHo 3Ha^eae 3a 3a^yByBaae Ha ^TH^HTe. Co npoMeHaTa Ha KOH3epBa^HCKHOT cTaTyc Ha HeKou BugoBH, h BoonmTo co HoBHTe nogaTC^u 3a pacnpocTpaHyBaaeTo u rojeMHHHTe Ha nonyj^HHTe Ha ^TH^HTe bo MaKegoHuja, 6eme noTpeÖHa peBH3uja Ha Mpe^aTa Ha 3ÜÜ 3a ga ce a^ypupaaT nocTojHHTe HH^opMa^HH 3a nogpa^jaTa bo 3eMjaTa, oöjaBeHH bo 1989 h 2000 roguHa. EugejKu $ayHaTa Ha ^TH^HTe bo PenyöjHKa MaKegoHuja e Mery HajMajKy npoy^eHHTe bo EBpona, u öugejKH ce ymTe bo rojeMa Mepa HegocTuraaT nogaTC^u 3a MHory BugoBH, noceÖHo ^TH^H-^eja^KH, HHBeHTapH3a^HjaTa rjjaBHo e HanpaBeHa Bp3 ocHoBa Ha nogaTC^HTe 3a HeKou 3acerHaTH hjh peTKH rpaöjHBH ^TH^H u HeKojKy gpyru noKpynHH BugoBH, KapaKTepucTMHH 3a MaKegoHcKHTe npegeju. KopucTeHHTe nogaTC^u 6ea coöupaHH bo TeKoT Ha pa3JHHHH cTyguu u npoeKTH, peajH3upaHH no 2000 roguHa. Og 314 BugoBH ^TH^H perucTpupaHH bo MaKegoHuja go geHec, 114 pegoBHo npucyTHH BugoBH bo MoMeHToB HMaaT HenoBojeH KOH3epBa^HCKH cTaTyc bo EBpona, a og hhb 84 rHe3gaT hjh BepojaTHo rHe3gaT bo MaKegoHuja. npu ceje^ujaTa Ha nogpa^jaTa 6ea KopucTeHH HeKojKy KpuTepuyMH pa3BueHH og BirdLife International 3a H36op Ha 3nn og rjioöajHo (KpuTepuyM A) u eBponcKo (KpuTepuyM B) 3Ha^eae, 3eMajKu ru npegBug BugoBHTe og raoöajeH HHTepec 3a 3a^yByBaae (A1), BugoBHTe orpaHH^eHH Ha noceÖHH 6homh (A3), 3Ha^ajHHTe coöupajumTa (A4, B1) h BugoBH co HenoBojeH KOH3epBa^HCKH cTaTyc (B2) hjh KoH^HTpupaHH bo EBpona (B3). BugoBHTe og raoöajeh HHTepec 3a 3a^yByBaae ru BKjy^yBaaT eruneTcKuoT Mpmojage^ (Neophron percnopterus), koj ce cMeTa 3a 3arpo3eH (EN) Ha raoöajho hhbo cnopeg HajHoBaTa ^pBeHa jucTa Ha IUCN Ha 3acerHaTH BugoBH, KagporaaBuoT nejHKaH (Pelecanus crispus) u ^pckhot opej (Aquila heliaca) (gBaTa qyBcTBHTejHH - VU) u MogpoBpaHaTa (Coracias garrulus) u mapeHoTo MyBap^e (Ficedula semitorquata) (6jH3y 3acerHaTH - NT). üoHaTaMy, bo MaKegoHuja ce cpeKaBaar h rpynu Ha BugoBH KapaKTepucTH^HH 3a eBpOnCKHOT BHcOKOnjaHHHcKH HjH MegHTepaHcKHOT 6hom. TpuTe rojeMH npupogHH e3epa ce 3Ha^ajHH coöupajHmTa Ha HerHe3ge^KH BogHH BugoBH ^TH^H, koh coHHHyBaaT HajMajKy 1% og ÖHoreorpa^cKara nonyj^uja Ha oggeiHuoT Bug, og koh HeKou (Ha np., KagporjiaBuoT neiuKaH, naTKaTa npeBe3 (Netta rufina)) bo MHory rojeM 6poj, noBeKe og geceTKpaTHo HagMHHyBajKu ro nparoT og 1%. 3a ceje^uja Ha nogpa^jara og eBponcKo 3Ha^eae 6ea KopucTeHu BKynHo 25 BugoBu koh pegoBHo ce npucyTHu bo MaKegoHuja, a 3a koh npucTanoT Ha 3a^yByBaae npeKy 3amTHTa Ha nogpa^ja ce cMeTa 3a coogBeTeH. ^paHH^HTe Ha nogpa^jara 6ea Ha^pTaHH ciegejKu H3pa3eHH reorpai^cKH KapaKTepucTHKu uiu u3oxuncu, 3a ga ru BKjy^yBaaT MecTaTa Ha rHe3geae u ucxpaHa Ha BHgoBHTe koh ru ucnojHyBaar KpuTepuyMHTe, 3a ^pcKHOT opei u eruneTcKuoT Mpmojage^ h nopaHemHHTe MecTa Ha rHe3geae (no 1991), 3eMajKu ru npegBug HHBHHTe noTpeöu og ^uBeaiumTa, KopucTeae Ha 3eMjumTeTo u noTpeÖHTe og ynpaByBaae. Pe3yjiTaToT BKiy^yBa 24 3nn, noKpuBajKu 6 907 km2 uiu 26,9% og noBpmuHaTa Ha MaKegoHuja: (1) fflap niaHHHa, (2) Cihbot Ha peKaTa PaguKa, (3) OxpugcKo E3epo, (4) npecnaHcKo E3epo, (5) ^eMupKanucKa Kiucypa, (6) ^ojpaHcKo E3epo, (7) ^oiuHaTa Ha 3jeTOBcKa PeKa, (8) TuKBemKuoT peruoH, (9) PeKaTa n^uaa - peKaTa neTpomHH^ - KpuBa PeKa, (10) npeog - fyraH^, (11) OcoroBcKu niaHHHH, (12) JaKynu^, (13) TaopcKa Kiucypa, (14) Obto noje, (15) PeKaTa TonoiKa - peKaTa Ea6yHa - peKaTa EperaIHH^a, (16) rpagcKo - PocoMaH - HeroTHHo, (17) MaHToBcKoT E3epTo h peKaTa KpuBa .^aKaBH^a, (18) ^oiHHara Ha peKaTa Pae^ (19) neiaroHuja, (20) MapuoBo, (21) TuKBemKo E3epo, (22) EomaBuja, (23) Ko^aHcKH opu3oBu nojuaa u (24) ^oihhot TeK Ha peKaTa Bapgap. Co ucKjy^oK Ha TpuTe nogpa^ja koh ru 3a$aKaaT niaHHHcKHTe MacuBu bo ceBepo3anagHHTe h ^HTpajHHTe geioBu Ha MaKegoHuja, u OxpugcKoTo h npecnaHcKoTo E3epo, nogpa^jara ce KOH^HTpupaHH rjiaBHo bo ^HTpajHHTe pugecTu u hh3hhckh geioBu Ha 3eMjara, on^aKajKu nogpa^ja co rHe3ga Ha rioöaiHo 3acerHaTu BugoBu. npo^HTOT Ha TepuTopuja noKpueHa co 3nn bo MaKegoHuja e peiaTHBHo bhcok cnopegeHo co BKynHuoT eBponcKu npoceK, ho e cnopegiuB co HeKoiKy 3eMju bo jyroucTo^Ha EBpona. noBpmuHaTa Ha nooggeiHu 3nn ce gBu^u og 25 km2 (TaopcKa Kiucypa) go 1 136 km2 (neiaroHuja), a 6pojoT Ha BugoBu koh ru ucnoiHyBaaT KpuTepuyMHTe og egeH (EomaBuja, Ko^aHcKH opu3oBu nojuaa) go 17 (PeKa n™aa - peKa neTpomHH^ - KpuBa PeKa). 22 nogpa^ja ucnoiHyBaaT HeKou og KpuTepuyMHTe 3a nogpa^ja og rjioöaiHo 3Ha^eae, Tpu nogpa^ja (OxpugcKoTo, npecnaHcKoTo h ^ojpaHcKOTo E3epo) ro HcnoiHyBaaT KpuTepuyMoT A4, ocyM nogpa^ja noggp^yBaaT 3Ha^aeH gei og ^o^yIa^HHTe Ha BugoBH KapaKTepucTH^HH 3a MeguTepaHcKuoT 6hom, a Tpu gpyru nogpa^ja noggp^yBaaT 3Ha^aeH gei og nonyj^HHTe Ha BugoBH KapaKTepucTH^HH 3a eBponcKuoT BucoKonjaHHHcKH 6hom. BugoBHTe og rjTOÖajeH HHTepec 3a 3a^yByBaae ce BKjy^eHH bo Mpe^aTa Ha 3nn Ha cjegHuoT Ha^HH: eruneTcKuoT Mpmojage^ Ha 13 nogpa^ja, ^pcKHOT opej Ha cegyM, KagporjaBuoT nejHKaH h jobwhckhot cokoj (Falco cherrug) Ha gBe, ^pHHOT Ko^yBap (Aythya nyroca) Ha Tpu, MogpoBpaHaTa Ha 10, ^pBeH0H0raTa BeTpymKa (Falco vespertinus) Ha Tpu h mapeHOTo MyBap^e Ha egHo nogpa^je. noeguHe^HH BugoBH koh ru HcnojHyBaaT KpuTepuyMHTe 3a nogpa^ja og eBponcKo 3Ha^eae ce npucyTHH Ha og 2 go 15 nogpa^ja. Mpe^aTa Ha 3nn BKjy^yBa 80-100% og Ha^H0HaIHHTe ^o^yIa^HH Ha raoSajHo 3acerHaTHTe BugoBH, a BKjy^eHocTa Ha ocTaHaTHTe BugoBH Bapupa og 5 go 100%, npu mTo 3a rojeM gej og BugoBHTe e Hag 40%. HeHaBogHyBaHHTe o6pa6oT!HBH noBpmuHH h npeogHHTe myMcKH ^ecTa^H ce goMHHaHTHH TunoBH Ha noKpoBHocT Ha 3eMjumTeTo, 3aegHo noKpuBajKu 32% og BKynHaTa noBpmuHa Ha 3nn. HanymTaaeTo Ha TpagH^H0HaIHH0T cTo^apcKH cucTeM mTo pe3yjTupa co HaMajyBaae Ha 6pojoT Ha cto^hhot $0Hg h 3apacHyBaae Ha nacumTaTa, KaKo h nocTaByBaaeTo cTa^H^H, TpyeaeTo h KpuBOjOBOT, ce cMeTaaT 3a Hajcepuo3HH 3aKaHH 3a BugoBHTe koh ru ucnojHyBaaT KpuTepuyMHTe, ocoöeHo 3a eruneTcKuoT Mpmojage^ h ^pcKHOT opej, h ce KIacH^H^HpaHH KaKo „bhcokh" Ha He noMajKy og 11 nogpa^ja. Ha^H0HaIHaTa 3amTHTa Ha nogpa^jara e HegoBOjHa, peajH3HpajKH ce hjh gejyMHo, hjh 6e3 coogBeTHH MepKH Ha 3amTHTa koh ce bo cuja, a MHory nogpa^ja ce ymTe HeMaaT HHKaKBa ^opMa Ha 3aKOHcKa 3amTHTa. Co 21% og Ha^H0HaIHaTa Mpe^a Ha 3amTHTeHH nogpa^ja Koja ce npeKjonyBa co 3nn, nocTojHuoT cucTeM Ha 3amTHTeHH nogpa^ja e HegoBOjeH 3a 3a^yByBaae Ha HajnpuopHTeTHHTe BugoBH. OcoöeHo nocTou npa3HHHa Kaj peruoHHTe bo HucKHTe gejOBH Ha 3eMjara, koh ce co HajBucoK 6poj Ha BugoBH og rjjoöajeH HHTepec 3a 3a^yByBaae. 6. References Apostolski, K. & Matvejev, S. 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Die ornithologischen Ergebnisse der Forschungsreisen, unternommen nach Mazedonien durch Prof. Dr. Doflein und Prof. L. Müller-Mainz in den Jahren 1917 und 1918. - Dultz & Co., München. Štumberger, B. & Velevski, M. (2002): White Stork Ciconia ciconia survey in Pelagonia indicates a decrease in its breeding population and colony disintegration. -Acrocephalus 23 (112): 67-74. Terrasse, J.F. & Terrasse, M. (1961): Ornithological impressions from Yugoslavia (1959). - L'Oiseau et R.F.O. 31 (1): 53-69. (in French) Terrasse, J.F. & Terrasse, M. (1961): Ornithological impressions from Yugoslavia (1959) (continuation and end). - L'Oiseau et R.F.O. 31 (2): 111-129. (in French) Thönen W. (2006): Pelagonien (Mazedonien) einst und heute (1). - Ornis 3: 10-11. Trpkov, B., Dončev, I. & Drozdovski, I. (1978): Lovečki priračnik. - Sojuz na lovečkite organizacii na Makedonija, Skopje. Vasic, V. (2009A): Study for the natural values of the Ezerani Nature Reserve: Birds. - Unpublished report to United Nations Development Programme (UNDP). Vasic, V. (2009B): Winter census of waterbirds of the pilot protected area »Tikvesh«. Report for the project "Strengthening the ecological, institutional and financial sustainability of Macedonia's national protected areas system. Management plan of the protected area »Tikveš«. - Ministry of Environment and Physical Planning of Republic of Macedonia & United Nations Development Programme (UNDP). Vasic, V. (2010): List of Birds of the National Park Galičica. Report for the management plan of the NP Galičica. -Public enterprise National park "Galičica", Ohrid. Vasic, V., Grubač, B., Su'ic, G. & Marinkovic, Š. (1985): The Status of Birds of Prey in Yugoslavia, with Particular Reference to Macedonia. pp. 45-53 In: Newton, I. & Chancellor, R.D. (eds.): Conservation Studies on Raptors, ICBP Technical Publication Series No. 5. -Princeton University Press, Cambridge. Vasic, V., Popovic, Z., Radakovic, M. & Ružic, M. (2009): Siva čiopa Apus pallidus u Srbiji i Makedoniji. - Ciconia 18: 132-142. Velevski, M. (2008): Evaluation of bird fauna at Matka Canyon, Macedonia. - Natura Montenegrina 7 (2): 369-380. Velevski, M. (2011): Non-critical checklist of birds of Macedonia. - [http://www.mes.org.mk/PDFs/Other/ Checklist%20of%20birds%20of%20Macedonia.pdf], 12/09/2011. Velevski, M. & Grubač, B. (2008): Distribution and estimation of the population size of the Short-toed Snake-eagle Circaetus gallicus in Macedonia. pp. 22-24 In: Proceedings of the 3rd Congress of Ecologists of the Republic of Macedonia with International Participation, 6-9 Sep 2007, Struga. - Special Issues of the Macedonian Ecological Society, Vol. 8, Skopje. Velevski, M. & Saveljic, D. (2010): Great Black-headed Gull Larus ichthyaetus. - Acrocephalus 31 (144): 57-71. Velevski, M. & štumberger, B. (2011A): List of ornithological references on Macedonia. - [http:// www.mes.org.mk/PDFs/Other/References%20on%20 birds%20of%20Macedonia%.pdf], 12/09/2011. Velevski, M. & štumberger, B. (2011B): Review of the references on birds of Macedonia. - Acrocephalus 31 (147): 283-291. Velevski, M., Dimitrovska, E. & Karčicki V. (2002A): Prilog kon ornitofaunata na Šar Planina. - Bilten na Istražuvačkoto društvo na studenti biolozi 2: 153-160. Velevski, M., Dimitrovska, E., Božič, L., Karčicki, V. & Pop-Trajkov, M. (2002B): Prilog kon ornitofaunata na masivot Jakupica. - Bilten na Istražuvačkoto društvo na studenti biolozi 2: 161-169. Velevski, M., Melovski, L., Maletik, V., Dzabirski, V. & Hristovski, š. (2003): Food availability for vultures (Aegypiinae) in Macedonia. Report for Black Vulture Conservation Foundation & Frankfurt Zoological Society. - Macedonian Ecological Society, Skopje. Velevski, M., Grubač, B. & Hallmann, B. (2008): Distribution and estimation of the population size of the Black Stork Ciconia nigra in Macedonia. - Ciconia 17: 14-19. Velevski, M., Pop-Trajkov, M,. Andevski, J. & Dimitrovska, E. (2003A): Istražuvanja na letniot aspekt na ornitofaunata na planinata Pelister. - Bilten na Istražuvačkoto društvo na studenti biolozi 3: 71-75. Velevski, M., Pop-Trajkov, M. & Andevski, J. (2003B): Podatoci za ornitofaunata na planinata Bistra. - Bilten na Istražuvačkoto društvo na studenti biolozi 3: 77-86. Wetlands International (2006): Waterbird Population Estimates. Fourth Edition. - Wetlands International, Wageningen. Arrived / Prispelo: 27.6.2011 Accepted / Sprejeto: 20.12.2011 Full list of species taken into consideration for identification of Important Bird Areas under B2 and B3 criteria, with population estimates, percentage of European population in Macedonia, median of population size in IBAs confirmed under the B2 & B3 criteria in the World Bird/Biodiversity Database (WBDB), and thresholds used in Macedonia given. Species denoted in bold were used for site identification. Vrste, upoštevane pri opredelitvi IBA-jev v okviru kriterijev B2 in B3, z ocenami njihovih populacij, odstotkom evropske populacije v Makedoniji, srednjo velikostjo populacije v IBA-jih, potrjenih v okviru kriterijev B2 in B3 v World Bird/Biodiversity Database (WBDB), in s populacijskimi pragovi, uporabljenimi v Makedoniji. Vrste, prikazane v mastnem tisku, so bile uporabljene za opredelitev območij. Species / Vrsta SPEC Site-based conservation suitable/ Območno varstvo primerno Population MK/ Populacija MK Population Europe/ Populacija Evropa Percentage of Europe population in Naivečie MK / Odstotek K , ' Na)yec,e , st. obmoci evropske , . ,r .. v okviru da populacije v MK (%) Max. No. of sites under B2 in B3 Median IBAs Europe / Srednja vrednost v evropskih IBA-jih (B2 & B3) B2 & B3 thresholds for MK/ populacijski prag v MK Falco naumanni i Yes 1,500 2,500 29,900 34,500 6.0 10 95 100 20 Aquila heliaca i Yes 30 40 850 1,400 3.2 5 3 4 2 Phalacrocorax pygmeus i Yes 60 120 28,000 39,000 0.4 5 80 no 30 Aythya nyroca i Yes 30 50 12,000 18,000 0.3 5 2-5 40 10 Falco cherrug i Yes 0 3 360 540 0.2 5 i 2 2 Crex crex i Yes 50 150 1,300,000 2,000,000 < O.I 5 40 50 20 Alectoris graeca 2 Yes 2,000 5,000 40,000 78,000 5-7 10 60 100 50 Ficedtila semitorquata 2 Yes 200 1,000 5,300 34.400 3-3 5 100 130 100 Accipiter brevipes 2 Yes 40 100 3,200 7,700 i-3 5 8 12 3 Lanius nubicus 2 Yes 300 500 35,000 100,000 0.7 5 10 20 10 Ciconia ciconia 2 Yes 650 800 180,000 220,000 0.4 5 80 no 30 Coracias garrulus 2 Yes 200 400 55,000 117,000 0.4 5 20 35 20 Ciconia nigra 2 Yes 35 45 7,800 12,000 0.4 5 10 10 3 Lanius minor 2 Yes 2,000 5,000 620,000 1,500,000 0.3 5 30 60 30 Phylloscopus bonelli 2 Yes 3,000 8,000 1,400,000 3,500,000 0.2 5 750 750 300 Aqtula pomarina 2 Yes 5 10 14,000 19,000 < O.I 5 8 9 2 Aythya ferina 2 Yes 0 20 210,000 440,000 < O.I 5 200 250 200 Lanius senator 2 No 5,000 15,000 480,000 1,200,000 1.1 Otus scops 2 No 1,800 4,000 210,000 440,000 0.9 Picus viridis 2 No 2,500 10,000 590,000 1,300,000 0.6 Caprinmlgus europaeus 2 No 2,000 5,000 470,000 1,000,000 0.5 Species / Vrsta SPEC Site-based conservation suitable/ Območno varstvo primerno Population MK/ Populacija MK Population Europe/ Populacija Evropa ofEuroSe Max. No. of , . . sites under B2 population in Naivečie MK / Odstotek K , ' Na)yec,e , st. obmoci evropske . . ' / .. v okviru da populacije v MK (%) Median IBAs Europe / Srednja vrednost v evropskih IBA-jih (B2 & B3) in B3 B2 & B3 thresholds for MK/ populacijski prag v MK Lulluk arborea 2 No 5,000 15,000 1,300,000 3,300,000 0.4 Miliaria calandra 2 No 30,000 100,000 7,900,000 22,000,000 0.4 Emberiza mehtiocephah 2 No 10,000 30,000 2,800,000 9,300,000 0.3 Carduelis cannabina 2 No 5,000 20,000 10,000,000 28,000,000 < O.I Emberiza horttdana 2 No 3,000 10,000 5,200,000 16,000,000 < O.I Phoetiicurus phoetiicurus 2 No 2,000 3,000 6,800,000 16,000,000 < O.I Oetiatithe hispatiica 2 No 1,300 2,500 1,400,000 3,300,000 < O.I Parus cristatus 2 No 1,000 2,500 6,100,000 12,000,000 < O.I Vanellus vanellus 2 No 50 150 1,700,000 2,800,000 < O.I Falco biarmicus 3 Yes 2-5 35 480 900 4-5 5 i 3 1-2 Circaetus gallicus 3 Yes 120 150 8,400 13,000 i-3 5 10 14 3 Monticola saxatilis 3 Yes 1,000 2,500 100,000 320,000 0.9 5 2-5 40 30 Buteo rufinus 3 Yes 80 120 8,700 15,000 0.9 5 8 10 4 Aquila chrysaetos 3 Yes 60 100 8,400 11,000 0.8 5 7 8 3 Neophron percnopterus 3 Yes 28 32 3,300 5,050 0.7 5 5 5 3 Bubo bubo 3 Yes 100 300 19,000 38,000 0.6 5 10 15 4 Ardeola ralloides 3 Yes 100 150 18,000 27,000 0.6 5 50 60 20 Falco tinnuncul.us 3 Yes 1,500 2,500 330,000 500,000 0.5 5 50 70 50 Burhinus oedicnemus 3 Yes 200 400 46,000 78,000 0.5 5 50 100 20 Monticola solitarius 3 Yes 400 1,000 120,000 260,000 0.4 5 15 30 20 Ixobrychus minutus 3 Yes 200 300 60,000 120,000 0.3 5 50 70 20 Nycticorax nycticorax 3 Yes 180 200 63,000 87,000 0.3 5 150 200 100 Aquila pennata 3 Yes 15 25 4,400 8,900 0.3 5 5 10 2 Melanocorypha cahtidra 3 Yes 20,000 50,000 10,000,000 24,000,000 0.2 5 4.850 9.450 5,000 Emberiza cia 3 Yes 2,000 5,000 1,300,000 4,100,000 O.I 5 100 150 150 Pyrrhocorax pyrrhocorax 3 Yes 40 120 43,000 110,000 O.I 5 100 150 20 Cahtidrelh brachydactyh 3 Yes 2,000 10,000 7,300,000 14,000,000 < O.I 5 * * * Species / Vrsta SPEC Site-based conservation suitable/ Območno varstvo primerno Population MK/ Populacija MK Population Europe/ Populacija Evropa Percentage of Europe Max. No. of sites under B2 population in . MK/Odstotek , , iNaJ™cJe evropske populacije v MK (%) št. območij v okviru B2 in B3 Median IBAs Europe / Srednja vrednost v evropskih IBA-jih (B2 & B3) B2 & B3 thresholds for MK/ populacijski prag v MK Riparia riparia 3 Yes 1,000 5,000 5,400,000 9,500,000 < o.i 5 10,000 10,000 1,000 Actitis hypoleticos 3 Yes 50 100 720,000 1,600,000 < o.i - * * * Alcedo atthis 3 Yes 20 100 79,000 160,000 < o.i 5 15 30 15 Cercotrichas gahetotes 3 Yes 20 100 32,000 96,000 < o.i < * * * Sternula albifrons 3 Yes 15 30 35,000 55,000 < o.i 5 70 120 20 Anas strepera 3 Yes 5 30 60,000 96,000 < o.i 5 30 45 30 Chlidonias hybrida 3 Yes 5 30 42,000 87,000 < o.i 5 100 140 100 Milvus migrans 3 Yes 3 10 64,000 100,000 < o.i 5 20 100 5 Botaurus stellaris 3 Yes i 10 34,000 54,000 < o.i 5 20 25 5 Anas qiierqueduh 3 Yes i 10 390,000 590,000 < o.i 5 340 430 300 Aythya ftiligtda 3 Yes 0 20 730,000 880,000 < o.i < * * 100 Chlidonias ttiger 3 Yes 0 20 83,000 170,000 < o.i 5 100 150 100 Ardea p urp urea 3 Yes 0 10 29,000 42,000 < o.i 5 80 100 80 Attas clypeata 3 Yes 0 5 170,000 210,000 < o.i < * * * Perdix perdix 3 No 25,000 100,000 1,600,000 3,100,000 2.2 Galerida cristata 3 No 50,000 150,000 3,600,000 7,600,000 1-7 Merops apiaster 3 No 4,000 20,000 480,000 1,000,000 1-3 Sylvia erassirostris 3 No 2,000 5,000 170,000 480,000 i.i Passer domesticus 3 No 500,000 1,000,000 63,000,000 130,000,000 0.8 Streptopelia turtur 3 No 25,000 60,000 3,500,000 7,200,000 0.8 Partis palustris 3 No 20,000 60,000 3,000,000 6,000,000 0.8 Anthus campestris 3 No 5,000 20,000 1,000,000 1,900,000 0.7 Sturtius vulgaris 3 No 100,000 500,000 23,000,000 56,000,000 0.6 Uptipa epops 3 No 5,000 10,000 890,000 1,700,000 0.6 Athene noctua 3 No 3,000 7,000 560,000 1,300,000 0.5 Lanius colltirio 3 No 15,000 50,000 6,300,000 13,000,000 0.3 Ahuda arvettsis 3 No 70,000 200,000 40,000,000 80,000,000 0.2 Species / Vrsta SPEC Site-based conservation suitable/ Območno varstvo primerno Population MK/ Populacija MK Population Europe/ Populacija Evropa Percentage of Europe Max. No. of sites under B2 population in . MK/Odstotek , , iNaJ™cJe evropske populacije v MK (%) št. območij v okviru B2 in B3 Median IBAs Europe / Srednja vrednost v evropskih IBA-jih (B2 & B3) B2 & B3 thresholds for MK/ populacijski prag v MK Delichon urbica 3 No 25,000 35,000 9,900,000 24,000,000 0.2 Oenanthe oenanthe 3 No 10,000 30,000 4,600,000 13,000,000 0.2 Hippolais pallida 3 No 5,000 20,000 3,300,000 6,700,000 0.2 Coturnix coturnix 3 No 5,000 10,000 2,800,000 4,700,000 0.2 Hirundo rustica 3 No 20,000 50,000 16,000,000 36,000,000 O.I Jynx torquilla 3 No 500 2,000 580,000 1,300,000 O.I Tyto alba 3 No 180 300 110,000 220,000 O.I Passer montanus 3 No 15,000 40,000 24,000,000 42,000,000 < O.I Muscicapa striata 3 No 1,000 3,000 14,000,000 22,000,000 < O.I Picus can us 3 No 50 250 180,000 320,000 < O.I Scolopax rusticola 3 No 30 90 1,800,000 6,6 00,000 < O.I Hippolais olivetorum non-SPECE Yes 500 3,000 11,000 23,000 7-7 10 70 no IOO Dendrocopos medius non-SPECE Yes 3,000 10,000 140,000 310,000 2.6 5 50 80 50 Turdus torquatus non-SPECE Yes 1,000 2,500 310,000 670,000 0.4 5 350 600 350 Regidus ignicapilh non-SPECE Yes 10,000 20,000 3,300,000 6,700,000 0.3 5 * * * Emberiza citrinelh non-SPECE Yes 30,000 100,000 18,000,000 31,000,000 0.2 5 * * * Ficedula albicollis non-SPECE Yes 2,000 8,000 1,400,000 2,400,000 0.2 5 2,200 4.650 2,000 Circus pygargus non-SPECE Yes IOO 140 35,000 65,000 0.2 5 20 45 20 Regidus regidus non-SPECE Yes 2,000 10,000 19,000,000 35,000,000 < O.I 5 * * * Acrocephalus scitpaceus non-SPECE Yes 2,000 5,000 2,700,000 5,000,000 < O.I 5 * * * Saxicoh rubetra non-SPECE Yes 1,000 5,000 5,400,000 10,000,000 < O.I 5 38O 1,000 400 Sitta neumayer non-SPECE Yes 500 2,000 2,000,000 6,100,000 < O.I 5 * * * A. schoenobaenus non-SPECE Yes 250 1,000 4,400,000 7,400,000 < O.I 5 2,500 3,000 2,000 Sylvia mehnocephah non-SPECE Yes 250 1,000 3,100,000 8,100,000 < O.I 5 * * * Carduelis spinus non-SPECE Yes 250 1,000 10,000,000 18,000,000 < O.I 5 * * * Columba oenas non-SPECE Yes 200 300 520,000 730,000 < O.I 5 IOO 280 150 Locustelh luscinioides non-SPECE Yes 50 250 530,000 800,000 < O.I 5 200 300 200 Species / Vrsta SPEC Site-based conservation suitable/ Območno varstvo primerno Population M K/ Populacija MK Population Europe/ Populacija Evropa ofEunroSee °f , . . sites under B2 population in &B,/Nai»ie MK / Odstotek K , ' Na)yec,e , st. obmoci evropske . . ' / .. v okviru d Z populacije v MK (o/o) 3 Median IBAs Europe / Srednja vrednost v evropskih IBA-jih (B2 & B3) B2 & B3 thresholds for MK/ populacijski prag v MK Acrocephalus palustris non-SPECE Yes 50 250 3,200,000 6,800,000 < O.I Larus michahellis non-SPECE Yes 50 100 210,000 256,000 < O.I Cygnus olor non-SPECE Yes 10 25 86,000 120,000 < O.I Emberiza cirlus non-SPECE No 30,000 100,000 2,000,000 5,200,000 i-7 Turdus viscivortis non-SPECE No 30,000 100,000 3,000,000 7,400,000 1.2 Dendrocopos syriacus non-SPECE No 3,000 15,000 530,000 1,100,000 0.9 Erithacus rubeciih non-SPECE No 300,000 700,000 43,000,000 83,000,000 0.7 Corvus monedula non-SPECE No 40,000 100,000 5,200,000 15,000,000 0.7 Ltiscinia megarhynchos non-SPECE No 30,000 100,000 4,200,000 12,000,000 0.7 Partis lugubris non-SPECE No 2,500 10,000 450,000 1,300,000 0.7 Partis caeriiUus non-SPECE No 120,000 200,000 20,000,000 44,000,000 0.5 Strix altico non-SPECE No 2,000 5,000 480,000 1,000,000 0.5 Certhia brachydactyla non-SPECE No 15,000 30,000 2,700,000 9,700,000 0.4 Turdus meruh non-SPECE No 100,000 300,000 40,000,000 82,000,000 0.3 Sylvia atricapilh non-SPECE No 60,000 150,000 25,000,000 49,000,000 0.3 Coin mba palumbus non-SPECE No 30,000 60,000 9,000,000 17,000,000 0.3 Tringilla coelebs non-SPECE No 300,000 500,000 130,000,000 240,000,000 0.2 Turdus p hi lomelos non-SPECE No 30,000 100,000 20,000,000 36,000,000 0.2 Cardtielis chhris non-SPECE No 30,000 50,000 14,000,000 32,000,000 0.2 Sylvia can till/ins non-SPECE No 2,000 5,000 1,400,000 3,200,000 0.2 Sylvia nisoria non-SPECE No 1,000 2,500 460,000 1,000,000 0.2 Pernis apivortis non-SPECE No 220 400 110,000 160,000 0.2 Sylvia communis non-SPECE No 10,000 20,000 14,000,000 25,000,000 < O.I Serintis serinus non-SPECE No 3,000 10,000 8,300,000 20,000,000 < O.I Prunella moduhris non-SPECE No 1,000 3,000 12,000,000 26,000,000 < O.I Sylvia borin non-SPECE No 250 1,000 17,000,000 31,000,000 < O.I Larus ridibtindtis non-SPECE No 0 250 1,500,000 2,200,000 < O.I Nadaljevanje dodatka 1 / Continuation of Appendix 1 * Few or no IBAs identified for the species under the B2 & B3 criteria in the World Bird/Biodiversity Database (WBDB) Population estimates refer to breeding pairs after BirdLife International (2004), except Falco naumanni, Coracias garrulus, Neophron percnopterus and Ficedula semitorquata, where data from the action plans were used (Inigo et al. 2008, Kovacs et al. 2008, Georgiev & Iankov 2010, Inigo & Barov 2010) SPEC — species of European conservation concern (SPEC 1 — European species of global conservation concern in Europe, i.e. classified as Critically Endangered, Endangered, Vulnerable, Near Threatened or Data Deficient under the IUCN Red List Criteria at a global level; SPEC 2 — species whose global populations are concentrated in Europe, and which have an Unfavourable conservation status in Europe; SPEC 3 — species whose global populations are not concentrated in Europe, but which have an Unfavourable conservation status in Europe; non-SPECE — species whose global populations are concentrated in Europe but which have a Favourable conservation status in Europe) (BirdLife International 2004) APPENDIX 2 / DODATEK 2 The overall classification of the major CORINE land cover types found within IBA boundaries in Macedonia Celotna razvrstitev glavnih tipov pokrovnosti in rabe tal (po CORINE land cover) znotraj meja IBA-jev v Makedoniji Level 1 / 1. nivo Level 2 / 2. nivo Level 3 / 3. nivo 1 Artificial surfaces/ 11 Urban fabric / Urbane površine 112 Discontinuous urban fabric/ Zgrajene površine Nesklenjene urbane površine 12 Industrial, commercial and transport units / Industrijske, trgovinske, transportne površine 13 Mine, dump and construction sites/ Rudniki, odlagališča, gradbišča 14 Artificial, non-agricultural vegetated areas / Umetno ozelenjene nekmetijske površine 121 Industrial or commercial units/ Industrija, trgovina 122 Road and rail networks and associated land / Cestno in železniško omrežje in pridružene površine 131 Mineral extraction sites/ Dnevni kopi, kamnolomi 132 Dump sites / Odlagališča 142 Sport and leisure facilities/ Površine za šport in prosti čas 2 Agricultural areas/ Kmetijske površine 21 Arable land / Njivske površine 22 Permanent crops / Trajni nasadi 23 Pastures / Pašniki 24 Heterogeneous agricultural areas/ Mešane kmetijske površine 211 Non-irrigated arable land/ Nenamakane njivske površine 212 Permanently irrigated land/ Namakane njivske površine 213 Rice fields / Riževa polja 221 Vineyards / Vinogradi 222 Fruit trees and berry plantations/ Sadovnjaki in nasadi jagodičja 231 Pastures / Pašniki 242 Complex cultivation patterns / Kmetijske površine drobnoposestniške strukture 243 Land principally occupied by agriculture, with significant areas of natural vegetation/ Pretežno kmetijske površine z večjimi območji naravne vegetacije Forest and semi natural areas / Gozdne in deloma ohranjene naravne površine 31 Forests / Gozdovi 32 Scrub and/or herbaceous vegetation associations/ Grmovje in/ali zeliščno rastlinstvo 33 Open spaces with little or no vegetation / Neporasle površine z malo ali brez vegetacije 311 Broad-leaved forest / Listnati gozd 312 Coniferous forest / Iglasti gozd 313 Mixed forest / Mešani gozd 321 Natural grasslands / Naravni travniki 322 Moors and heathland / Barja in resave 323 Sclerophyllous vegetation/ Sklerofilno rastlinstvo 324 Transitional woodland-shrub/ Grmičast gozd 331 Beaches, dunes, sands/ Plaže, sipine in peščene površine 332 Bare rocks / Golo skalovje 333 Sparsely vegetated areas/ Redko porasle površine 4 Wetlands/ Močvirnate površine 41 Inland wetlands / Celinska močvirja 411 Inland marshes / Celinska barja 5 Water bodies/ Vodne površine 51 Inland waters / Celinske vode 511 Water courses / Vodotoki in kanali 512 Water bodies / Mirujoča voda 3 APPENDIX 3 / DODATEK 3 List from the national Emerald Database, used for identification of the main threats to birds and their importance in Macedonian IBAs Seznam iz nacionalne baze podatkov Emerald, uporabljen za opredelitev najpomembnej{ih dejavnikov ogrožanja ptic in njihovega vpliva v makedonskih IBA-jih Code/ Koda Threat / Dejavnik ogrožanja 100 Cultivation / Obdelovalne površine 101 Modification of cultivation practices / Spreminjanje obdelovalnih praks 110 Use of pesticides / Uporaba pesticidov 141 Abandonment of pastoral systems / Opuščanje pašništva 160 General forestry management / Splošno gozdarsko upravljanje 161 Forest planting / Pogozdovanje 162 Artificial planting / Zasajevanje tujerodnih dreves 167 Forest exploitation without replanting / Izkoriščanje gozdov brez ponovnega zasajevanja 210 Professional fishing / Poklicni ribolov 220 Leisure fishing / Prostočasni ribolov 230 Hunting / Lov 242 Taking from nest (falcons) / Odvzemanje iz gnezd (sokoli) 243 Trapping, poisoning, poaching / Lov s pastmi, zastrupljanje, divji lov 290 Hunting, fishing or, collecting activities not referred to above / Lov, ribolov ali odvzemanje osebkov, ki ni navedeno zgoraj 300 Sand and gravel extraction / Izkopavanje peska in proda 301 Quarries / Kamnolomi 331 Open cast mining / Površinsko rudarstvo 400 Urbanised areas, human habitation / Urbanizirana območja, človeška bivališča 403 Dispersed habitation / Razkropljena bivališča 410 Industrial or commercial areas / Industrijske ali trgovske površine 501 Paths, tracks, cycling tracks / Poti, kolovozi, kolesarske steze 502 Motorways, roads / Avtoceste, ceste 503 Railway lines, TGV / Železniški tiri, TGV 505 Airport / Letališče 511 Electricity lines / Daljnovodi 530 Improved access to site / Povečan dostop na območje 600 Sport and leisure structures / Športne in prostočasne zgradbe 624 Mountaineering, rock climbing, speleology / Gorništvo, plezanje, speleologija 701 Water pollution / Onesnaževanje voda 730 Military maneuvers / Vojaške vaje 803 Infilling of ditches, dykes, ponds, marshes or pits / Zasipavanje jarkov, vodnih teles, močvirij ali jam 810 Drainage / Osuševanje 952 Eutrophication / Evtrofikacija 960 Interspecific faunal relations / Medvrstni odnosi APPENDIX 4 / DODATEK 4 Detailed calculation of threat scores for seperate IBAs. Podroben izračun dejavnikov ogrožanja za posamezne IBA-je. Site / Območje Code/ Koda Effect habitat/ Učinek habitat Effect species/ Učinek vrsta Spatial scale/ Obseg Realization/ Časovni okvir Score/ Vsota Threat impact/ Vpliv Šar Planina Mountain 141 160 960 230 243 501 530 167 624 600 1 2 2 1 2 2 2 1 2 1 2 2 2 1 2 2 3 3 3 3 2 2 2 2 1 1 3 3 3 3 3 3 3 3 3 2 8 8 8 7 7 7 7 6 6 5 high high high medium medium medium medium medium medium low Radika River Catchment 960 141 160 243 410 501 624 530 1 1 1 1 1 2 2 1 2 2 1 1 1 3 2 2 1 2 1 1 1 3 3 3 3 2 3 3 2 8 7 6 6 6 5 5 4 high medium medium medium medium low low low Lake Ohrid 600 803 3 3 2 2 2 2 3 3 8 8 high high Lake Prespa 100 701 952 243 600 803 3 2 2 1 2 1 2 2 2 1 2 2 3 3 2 2 1 3 3 3 3 3 3 8 8 8 7 6 6 high high high medium medium medium Demir Kapija Gorge 243 141 230 160 502 624 301 410 730 400 2 2 3 1 1 3 2 2 2 2 2 2 2 2 1 3 3 3 2 2 2 1 3 1 1 3 3 3 3 2 3 3 1 3 3 9 8 8 7 7 7 6 6 6 5 high high high medium medium medium medium medium medium low Lake Dojran 410 210 600 2 3 3 3 3 3 2 3 2 3 9 8 8 high high high Zletovska River Valley 141 243 101 1 1 3 3 2 3 3 1 3 3 3 9 9 6 high high medium Nadaljevanje dodatka 4 / Continuation of Appendix 4 Site / Območje Code/ Koda Effect habitat/ Učinek habitat Effect species/ Učinek vrsta Spatial scale/ Obseg Realization/ Časovni okvir Score/ Vsota Threat impact/ Vpliv 410 1 2 2 2 6 medium Tikveš Region 110 243 141 511 502 2 2 2 3 2 2 2 2 3 3 2 2 1 3 3 3 3 3 9 8 7 7 6 high high medium medium medium Pčinja - Petrošnica - Kriva Reka Rivers 141 243 230 160 242 410 502 503 701 1 2 2 2 2 1 2 2 1 2 2 2 2 2 1 3 3 3 1 1 2 2 2 2 3 3 3 3 3 2 2 2 3 8 8 7 6 6 6 6 6 6 high high medium medium medium medium medium medium medium Preod - Gjugjance 141 511 410 502 505 2 2 2 2 3 3 3 3 3 3 3 3 2 2 2 3 3 2 2 2 9 9 7 7 7 high high medium medium medium Osogovo Mountains 160 242 403 502 301 2 1 2 2 2 2 2 2 2 3 3 2 2 1 3 3 3 3 3 8 8 7 7 6 high high medium medium medium Jakupica Mountain 141 243 960 230 2 2 2 2 1 3 3 3 2 3 3 3 3 8 8 8 6 high high high medium Taor Gorge 960 410 502 162 230 301 501 503 530 701 220 3 2 2 2 1 2 2 1 3 3 2 2 2 3 2 2 2 1 1 3 3 3 2 2 2 2 2 2 3 2 3 2 3 3 3 2 3 3 3 3 3 9 8 8 7 7 7 7 7 7 7 6 high high high medium medium medium medium medium medium medium medium Ovče Pole 110 141 511 243 2 2 3 3 3 2 3 3 3 3 3 3 3 3 9 9 9 8 high high high high Nadaljevanje dodatka 4 / Continuation of Appendix 4 Site / Območje Code/ Koda Effect habitat/ Učinek habitat Effect species/ Učinek vrsta Spatial scale/ Obseg Realization/ Časovni okvir Score/ Vsota Threat impact/ Vpliv 161 230 290 410 2 1 2 1 2 2 2 3 2 2 3 3 3 2 7 7 7 6 medium medium medium medium Topolka - Babuna -Bregalnica Rivers 141 243 960 100 162 230 403 624 301 1 1 2 2 2 2 2 2 2 2 1 2 2 2 3 3 3 2 2 3 2 2 1 3 3 3 3 3 3 3 3 3 8 8 8 7 7 7 7 7 6 high high high medium medium medium medium medium medium Gradsko - Rosoman -Negotino 110 243 511 100 161 730 2 1 2 2 2 2 2 2 2 3 3 3 2 2 1 3 3 3 3 3 3 8 8 8 7 7 6 high high high medium medium medium Lake Mantovo and Kriva Lakavica River 242 243 331 701 3 2 2 1 2 2 2 3 1 2 3 3 3 3 7 7 7 7 medium medium medium medium Raec River valley 960 141 301 403 243 2 1 2 2 2 3 2 2 3 2 1 2 1 3 3 3 3 3 8 7 7 7 6 high medium medium medium medium Pelagonia 100 110 141 511 803 2 2 2 1 3 3 3 3 2 3 3 3 3 3 3 3 3 2 3 9 9 9 8 8 high high high high high Mariovo 141 243 960 230 301 410 530 624 2 2 3 2 3 3 3 2 2 3 2 1 3 3 3 3 2 3 2 1 3 3 3 3 3 1 3 3 9 9 9 8 7 7 7 5 high high high high medium medium medium low Lake Tikveš 243 403 141 2 2 3 2 2 3 3 2 3 3 3 9 8 7 high high medium Nadaljevanje dodatka 4 / Continuation of Appendix 4 Site / Območje Code/ Koda Effect habitat/ Učinek habitat Effect species/ Učinek vrsta Spatial scale/ Obseg Realization/ Časovni okvir Score/ Vsota Threat impact/ Vpliv 160 511 2 2 2 2 2 3 3 7 7 medium medium Bošavija 141 243 160 511 400 2 2 2 1 3 3 2 1 1 3 3 2 2 2 3 3 3 3 3 9 9 7 7 6 high high medium medium medium Kočani Rice Fields 110 511 101 1 1 2 2 2 2 3 2 2 3 3 2 8 7 6 high medium medium Lower Vardar 300 410 810 511 3 3 3 1 3 2 2 2 2 3 2 2 3 2 3 3 8 8 8 7 high high high medium * The combined level of the threat is calculated by summing up the (1) Effect habitat / Effect species, (2) Spatial scale and (3) Realization values. Under the (1) the highest value of both is taken into consideration in calculation of the score. & APPENDIX 5 / DODATEK 5 o Overview of all qualifying and other important bird species in Macedonian IBAs with criteria, season in which species qualify, number of sites occupied, total IBA populations and percentage of national population included in the IBA network given Pregled vseh kvalifikacijskih in drugih pomembnih vrst ptic v IBA-jih v Makedoniji s podanimi kriteriji, obdobjem pojavljanja, v katerem vrste izpolnjujejo kriterije, številom zasedenih območij, velikostjo populacije na vseh IBA-jih in odstotkom nacionalne populacije, vključene v IBA-omrežje 3 o p 3 Cd p_ (33 £ K Species / Vrsta Criteria/ Kriteriji Season/ Sezona No. of sites — qualifying/ St. območij — kvalifikacijska No. of sites - listed / Št. območij — navedena Total IBA population/ Skupna IBA populacija Year/ Leto Percentage of MK population in IBAs / Odstotek MK populacije v IBA-jih Pelecanus crispus Al, A4i, Bli N 2 3 300-1000 ind. 2002-2010 100 Neophron percnopterus Al, B2 B 13 13 22-33 2005-2010 95 Coracias garrulus Al, B2 B 7 IO 80-200 2002-2009 40-50 Aquila heliaca Al, B2 B 6 7 28-40 2006-2010 80-90 Ficedula semitorquata Al B i 2 20-70 2009 7-10 Falco vespertinus Al? M o 3 70-260 ind. 2002-2010 40-70 Alectoris graeca A3, B2 B IO u unknown 2009-2010 unknown Lanius nubicus A3, B2 B 6 6 unknown 2007-2010 unknown Emberiza melanocephala A3 B 8 8 unknown 2000-2010 unknown Oenanthe hispanica A3 B 8 8 unknown 2000-2010 unknown Sylvia cantillans A3 B 8 8 unknown 2000-2010 unknown Sitta neumayer A3 B 7 7 unknown 2000-2010 unknown Hippolais olivetorum A3 B 3 3 unknown 2000-2010 unknown Montifringilla nivalis A3 B 3 3 unknown 1998-2004 unknown Prunella collaris A3 B 3 3 unknown 2002-2006 unknown Pyrrhocorax graculus A3 B 3 3 300-550 2005-2010 50-60 Fichodroma muraria A3 B 3 3 20-40 1999-2004 60-70 Pelecanus onocrotalus A4i, Bli N i 2 200-550 ind. 2008-2010 100 Falco naumanni A4ii, Bliii, B2 B 9 IO 1625-1975 2002-2003 80-100 Mergus merganser Bli B 2 2 31-53 2006-2010 100 Fulica atra Bli W I 3 23000-70000 ind. 1987-2011 90-100 Podiceps nigricollis Bli W I 2 1400-7000 ind. 1988-2004 95-100 Netto, rufma Bli W I I 350-7000 ind. 1987-2011 100 Aquila chrysaetos B2 B 5 H 29-41 2005-2010 40-50 Bubo bubo B2 B 5 13 50-89 2005-2010 30-50 3 g S 1 p f* rti Cd 0- • § ° 5. jo p c •• co oo > s* o< m " , 0 H £ % EL 2 1—' M p O O "u. p_ w trt In e H 1 § T? z; p Q 3 c? 0< S S a w O r< ŠT a (33 O N< o< P? (33 Species / Vrsta Criteria / Kriteriji Season/ Sezona No. of sites — qualifying/ St. območij — kvalifikacijska No. of sites - listed / Št. območij — navedena Total IBA population/ Skupna IBA populacija Year/ Leto Percentage of MK population in IBAs / Odstotek MK populacije v IBA-jih Circaetus gallicus B2 B 5 13 49-78 2007-2010 45-55 Falco biarmicus B2 B 5 9 14-19 2005-2009 50 Buteo rufinus B2 B 4 13 45-63 2005-2010 50-60 Ciconia nigra B2 B 4 8 13-19 2005-2010 35-45 Accipiter brevipes B2 B 3 6 9-21 2004-2009 20-25 Burhinus oedicnemus B2 B 3 5 unknown 2002-2010 unknown Ciconia ciconia B2 B 3 3 420-470 2002-2011 50-60 Monticola saxatilis B2 B 2 5 unknown 2000-2010 unknown Crex crex B2 B 2 2 50-150 2010 50-75 Ixobrychus minutus B2 B 2 2 80-230 2000-2009 40-70 Lanius minor B2 B 2 2 unknown 2002-2010 unknown Monticola solitarius B2 B 2 2 unknown 2000-2010 unknown Aythya nyroca B2 B i 3 15-30 1998-2008 40-75 Phalacrocorax pygmeus B2 B i 3 60-120 1993-2000 100 Sternula albifons B2 B i i 15-30 2008 100 Riparia riparia B2 B i i 800-1200 2002-2010 20-80 Pyrrhocorax pyrrhocorax B2? B O 3 unknown 1999-2004 unknown Botaurus stellaris B2? B O i 2-6 1998-2006 30-100 Falco tinnunculus B2? B O 5 unknown 2000-2010 unknown Circus pygargus B3 B i 3 66-100 2002-2010 65-70 Falco peregrinus N B o n 23-35 2006-2010 25-50 Gyps fulvus N B o 8 19-35 2006-2010 100 Ardea cinerea N B o 3 160-210 2002-2010 70-95 Aythya fuligula N W o 3 500-10000 ind. 1987-1999 95-100 Eremophila alpestris N B o 3 unknown 2000-2010 unknown Milvus migrans N B o 3 2-3 2007-2010 30-70 Anas strepera N B o 2 2-15 1995-2002 40-50 Aythya ferina N W o 2 2000-7000 ind. 1987-2000 80-100 Falco cherrug N B o 2 0-2 2003-2010 60-100 Podiceps cristatus N B o 2 100-700 2000-2010 80-95 >A £ s G >n IS u p o p M d O taB i-J £ A on/ BA ija M .2 i-i ij - J g -q pSp 8 ,c/3 I rt ^ C iu u <4- -Ö q oe e ■ % E £ o _D <3 i "Üb.! I .5 iu : ^ § a S j* alb i o - i ^ > I >CO Jd rt S £ u w £ O o H O O O VD O O O ^ N N N O d n o o o o o o zzzzzz 5 "li 5 saga Review of the references on birds of Macedonia Pregled virov o pticah Makedonije Metodija Velevski1 & Borut Stumberger2 1 Macedonian Ecological Society, P.O. Box 162, MK-1000 Skopje, Macedonia, e-mail: velevski@mes.org.mk 2 EuroNatur, Konstanzer Str. 22, D-78315 Radolfzell, Germany, e-mail: stumberger@siol.net This list includes probably more than 90% of all the material containing data on birds of the Republic of Macedonia. This time, the references in their original language are presented, with (C) denoting that the original work was published in Cyrillic alphabet. 268 references depict Macedonian ornithology and its history, showing its ups and downs at the same time. The references presented herewith are for information purposes only. As no complete information has been at hand for certain references, some mistakes are possible. The last update was made on 14 Dec 2011. Online version of this review is available on the web page of the Macedonian Ecological Societya) where it is regularly updated. You are kindly requested to report on all possible/necessary corrections, supplements or new references that embrace original data on birds of Macedonia, to the authors. The next step to be made in the ensuing years is preparation of the authors' and species' index, key words and list of localities (regions). Our cordial thanks to you all. 1. Apostolski, K. &Jovetic, R. (1967): Uticaj ornitofaune na gustinu populacije riba u Dojranskom Jezeru. — Izdanija Zavod za ribarstvo na NR Makedonija 3 (2): 169-175. (C) 2. Apostolski, K. & Jovetic, R. (1967): Vlijanie na ishranata na pticite močvarici vrz ribnite populacii od Dojranskoto Ezero. Završen izveštaj. — Zavod za ribarstvo na SR Makedonja, Skopje. 3. Apostolski, K. & Matvejev, S. (1955): Lov riba u ogradama pomocu ptca na Dojranskom jezeru. — Izdanija Zavod za ribarstvo na NR Makedonija 1 (3): 29—65. 4. Banzhaf, W. (1931): Ein Beitrag zur Avifauna Mazedoniens. — Journal für Ornithologie 79 (3): 319— 323. 5. Benson, S.V., Irving, W.M, McDowel, C., Higginbottom, C. & Lind, P.B. (1960): Birds seen in Yugoslavia. — Larus 14: 190—194. 6. Beran, V., Škorpikova, V., Prašek, V. & Dostal, M. (2007): Observation of Greater Flamingo Phoenicopterus ruber in Macedonia in 2007. — Ciconia 16: 85. 7. Birdlife International (2004): Birds in Europe: population estimates, trends and conservation status. BirdLife Conservation Series No. 12. — BirdLife International, Cambridge. 8. Bodenstein, G. (1949): Zur Ethologie und Biologie der Türkentaube (Streptopelia d. decaocto Friv.). — Ornithologische Beobachter 46 (4): 107—116. 9. Bodenstein, G. (1943): Zur Flugweise des Rötelfalken (Falco n. naumanni Fleischer). — Ornithologische Monatsberichte 51 (5/6): 157—158. 10. Bodenstein, G. & Kroymann, B. (1967): Die Ergebnisse der Mazedonien-Exkursion der Ornithologischen Gesellschaft in Bayern im Mai/Juni 1966. — Anzeiger der Ornithologischen Gesellschaft in Bayern 8 (2): 134—157. 11. Bojabievski, K. (1985): Orlovi u Makedoniji: Zaštita za ravnotežu. — Lovački vijesnik. 12. Božič, L. (2001): Lesser Kestrel Falco naumanni. — Acrocephalus 22 (108): 183—184. 13. Božič, L. (2001): Long-legged Buzzard Buteo rufinus. — Acrocephalus 22 (108): 183. 14. Corti, U.A. & Simon, A. (1970): Ornithologische Beobachtungen in Macedonien 1968. — Monticola 26 (2): 97—110. 15. Dangel, M. (1973): Ornithologische Beobachtungen am Dojran-See. — Ornithologische Mitteilungen 25: 73—75. 16. Danko, S. & Szilard, P. (1971): Ornithologische Beobachtungen in Mazedonien, mit besonderer Berücksichtigung der Greifvögel. — Ornithologische Mitteilungen 23 (1): 9—18. 17. Delic, S. (1948): Ornitološka ekskurzija na Šar-planinu. — Larus 2: 102—105. 18. Dijksen, A. & Dijksen, S. (1984/1985): Ornithological observations in Macedonia, Yugoslavia in Autumn 1983. — Larus 36/37: 265—282. 19. Dijksen, S. & Dijksen, A. (1984/1985): Some observations of birds in the Ohrid Lake area (Yugoslavia) in May 1980. — Larus 36/37: 253—264. 20. Dimovski, A.S. (1955): Ornithogeographischer Vergleich zwischen Nord- und Südmazedonien. — Acta Musei Macedonici Scientiarum Naturalium 3 (6): 159—179. 21. Dimovski, A.S. (1957): Ptici na Osogovo Planina. — Acta Musei Macedonici Scientiarum Naturalium 5 (3): 33—59. (C) 22. Dimovski, A.S. (1959): Pelikani u Makedoniji. — Zaštita prirode 16: 36—38. 23. Dimovski, A.S. (1960): Rasprostranenieto na Phylloscopus bonelli orientalis (Brehm) na Balkanskiot Poluostrov. — Fragmenta Balcanica 3 (5): 31—35. (C) 24. Dimovski, A.S. (1967): Biogeografska i ekološka karakteristika na Skopska kotlina. — Godišen Zbornik na Prirodno-matematički fakultet na Univerzitetot vo Skopje 20: 5—70. (C) 25. Dimovski, A.S. (1971): Sezonski izmeni na ornitofaunata vo sostoinata na prnar (Quercus coccifera) vo Makedonija. — Godišen zbornik na Institutot za biologija 23: 45-54. (C) 26. Dimovski, A.S. (1971): Zoocenološki istražuvanja na stepskite predeli vo Makedonija. - Godišen zbornik na Institutot za biologija 23: 25-43. (C) 27. Dimovski, A. (1972): Izmeni vo sostavot na ornitofaunata na Skopskata kotlina. - Acta Musei Macedonici Scientiarum Naturalium 13 (3): 41-64. (C) 28. Dimovski, A. & Matvejev, š. (1955): Ornithologische Forschungen in der VR Macedonien. - Arhiv bioloških nauka 1/2: 121-138. 29. Doflein, F. (1921): Mazedonien. Erlebnisse und Beobachtungen eines Naturforschers im Gefolge des Deutsches Heeres. - Gustav Fischer, Jena. 30. DonČev, I. (1964): Prilog morfologiji poljske jarebice Perdix perdix L. u Makedoniji. - Lovački savez SR Makedonije, Skopje. 31. Drummond, H.M. (1846): List of the Birds observed to winter in Macedonia, during a two months' Shooting Excursion in the Interior during the winter of 1845-46. - Annals & Magazine of Natural History 18: 10-15. 32. Eber, G. (1967): Wasservögelbeobachtungen im März 1967 aus Nordgriechenland und Südjugoslawien. -Anzeiger der Ornithologischen Gesellschaft in Bayern 8 (2): 158-165. 33. Elwes, H.J. & Buckley, T.E. (1870): A list of the Birds of Turkey. - Ibis 6: 59-76, 188-201, 327-339. 34. Farmahem (2010): Study for revalorization of natural values of protected area "Tikves" Strict Nature Reserve. Report to UNDP and Ministry of Environment and Physical Planning of Republic of Macedonia. -Farmahem, Skopje. 35. Fehringer, O. (1922): Die Vogelwelt Macedoniens. Forschungsreise auf dem macedonischen Kriegsschauplatz 1917 und 1918. - Journal für Ornithologie 70: 89-123. 36. Fehringer, O. (1920): Vogelzug in Macedonien Frühjahr 1918. - Ornithologische Monatsberichte 28: 55-57. 37. Fremuth, W., Bino, T., Bego, F., Jorgo, G., Micevski, B., Anastasovski, V., Tzvetkov, T., Hristov, I., Schneider-Jacoby, M. & Shumka, š. (2000): Four years of simultaneous wintering waterbird census at the Ohrid and Prespa Lakes 1997-2000. pp. 30-39 In: Proceedings of the International Symposium »Sustainable development of Prespa Region«, 23-25 Jun 2000, Oteševo. - Macedonian Ecological Society and Society "Prespa", Skopje. 38. Ganso, M. (1962): Beobachtungen aus Jugoslawien und Nordgriechenland. - Egretta 5 (2): 60-64. 39. Geiger, š., Kratzer, R. & Stopper, H. (1974): Vogelkundliche Frühjahrsbeobachtungen in Macedonien. - Ornithologische Mitteilungen 26: 133-141. 40. Gengler, J. (1918): Der serbisch-mazedonische Kolkrabe. - Ornithologische Monatsberichte 26: 110. 41. Gengler, J. (1920): Balkanvögel. Ein ornithologisches Tagebuch. - Verlagsbuchhandlung Pierer, Altenburg & Leipzig. 42. Gengler, J. (1921): Der Gefiederwechsel des mazedonischen Steinhuhs. - Ornithologische Monatsberichte 29: 68-69. 43. Gengler, J. & Stresemann, E. (1919): Dryobates major balcanicus Geng. & Stres. subsp. n. - Anzeiger der Ornithologischen Gesellschaft in Bayern 1: 2. 44. Geroudet, P. (1965): La Buse feroce, Buteo rufinus, au defile de Demir-Kapija. - Larus 19: 156-157. 45. Glegg, W.E. (1924): A list of the Birds of Macedonia. - Ibis 66 (1): 46-86. 46. Goetz, L. (1954): Bird photographs taken during my journey in Yugoslavia. - Larus 8: 138-141. 47. Gregori, J. (1976/1977): Kormorani na Prespanskem jezeru. - Proteus 39 (9/10): 327-332. 48. Grubac, B. (1994): La situation di Faucon lanier Falco biarmicus in Mediterranee et specialement das le centre des Balkans. pp. 127-134 In: Muntaner, J. & Mayol, J. (eds.): Raptors biology and conservation of mediterranean raptors. Proceedings of the 6th Congress on Biology and Conservation of Mediterranean Raptors, 22-25 Sep 1994, Palma de Mallorca. - SEO/ BirdLife, Madrid. 49. Grubac, B. (1997): The present status of vultures Aegypiinae in Central Balkans. pp. 93-103. In: Actas del II congreso internacional sobre Aves Carroneras. -Canizares-Solan de Cabras, Cuenca. 50. Grubac, B.R. (1991): Situation actuelle des Vautors (Aegypiinae) en Macedoine. pp 139-145 In: Proceedings from the Congreso Internacional sobre Aves Carroneras. - Aedanat - Coda - Icona, Madrid. 51. Grubac, B., Velevski, M., Lisicanec, T., Lisicanec, E., Rolevski, D. & Andevski, J. (2007): The decreasing population size of Griffon Vulture (Gyps fulvus) in Macedonia and assesment of conservatuion measures. pp. 101-102 In: Abstract book from the 3rd Congress of the Ecologists of Macedonia, with international participation, 6-9 Oct 2007, Struga. 52. Grubač, B. 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(2008): Distribution and estimation of the population size of the Short-toed Snake-eagle Circaetus gallicus in Macedonia. pp. 2224 In: Proceedings of the 3rd Congress of Ecologists of the Republic of Macedonia with International Participation, 6-9 Sep 2007, Struga. - Special Issues of the Macedonian Ecological Society, Vol. 8, Skopje. 259. Velevski, M. & Saveljic, D. (2010): Great Black-headed Gull Larus ichthyaetus. - Acrocephalus 31 (144): 57-71. 260. Velevski, M. Dimitrovska, E. & Karčicki V. (2002): Prilog kon ornitofaunata na Šar Planina. -Bilten na Istražuvačkoto društvo na studenti biolozi 2: 153-160. (C) 261. Velevski, M., Dimitrovska, E., Božič, L., Karčicki, V. & Pop-Trajkov, M. (2002): Prilog kon ornitofaunata na masivot Jakupica. - Bilten na Istražuvačkoto društvo na studenti biolozi 2: 161-169. (C) 262. Velevski, M., Pop-Trajkov, M., Andevski, J. & Fajdiga, B. (2002): Prvi podatoci za ornitofaunata na planinata Ogražden. - Bilten na Istražuvačkoto društvo na studenti biolozi 2: 171-177. (C) 263. Velevski, M., Pop-Trajkov, M,. Andevski, J. & Dimitrovska, E. (2003): Istražuvanja na letniot aspekt na ornitofaunata na planinata Pelister. - Bilten na Istražuvačkoto društvo na studenti biolozi 3: 71-75. (C) 264. Velevski, M., Pop-Trajkov, M. & Andevski, J. (2003): Podatoci za ornitofaunata na planinata Bistra. — Bilten na Istražuvačkoto društvo na študenti biolozi 3: 77-86. (C) 265. Velevski, M., Grubač, B. & Hallmann, B. (2008): Distribution and estimation of the population size of the Black Stork Ciconia nigra in Macedonia. — Ciconia 17: 14—19. 266. Velevski, M., Hallmann, B., Grubač, B., Lisičanec, T., Stoynov, E., Lisičanec, E., Avukatov, V., Božič, L. & Stumberger, B. (2010): Important Bird Areas in Macedonia: Sites of global and European Importance. — Acrocephalus 31 (147): 181—282. 267. Viereck, von M. (1917): Ornithologische Beobachtungen vom Kriegsschauplatz in Mazedonien. — Ornithologische Monatsschrift 42 (9): 233—246. 268. Vogrin, M. (1990): Ornitološka opažanja is osrednje Makedonije. — Acrocephalus 11 (45): 47—52. Seznam vsebuje verjetno več kot 90 % celotnega gradiva s podatki o pticah Republike Makedonije. Tokrat so viri navedeni v njihovem izvirnem jeziku, kjer (C) pomeni, da je delo v originalu objavljeno v cirilici. 268 virov opisuje makedonsko ornitologijo in njeno zgodovino ter kaže na njene vzpone in padce. Viri, navedeni v tem seznamu, so zgolj informativnega značaja. Ker so bili za nekatere vire uporabljeni še nepopolni podatki, so v besedilu možne določene napake. Zadnja posodobitev besedila je bila opravljena 14.12.2011. Spletna verzija tega prispevka je dostopna na spletni strani Makedonskega ekološkega društvaa), kjer se tudi redno posodablja. Prosiva vas, da vse morebitne popravke, dopolnila ali nove vire, ki vključujejo izvirne podatke o pticah Makedonije, sporočite na naslove avtorjev. Korak naslednjih let je izdelava indeksa avtorjev, vrst, ključnih besed in seznama lokalitet (regij). Hvala. a) http://www.mes.org.mk/PDFs/0ther/References%20on%20 birds%20of%20Macedonia.pdf Arrived / Prispelo: 9.12.2011 Accepted / Sprejeto: 20.12.2011 Kazalo letnika 31 (2010), št. 144-147: str. 1-301 Index of Volume 31 (2010), No. 144-147: pp 1-301 Kazalo avtorjev / Index of authors Uvodnik / Editorial Probst, R.: Important sites for migrating raptors in the Eastern Alps [Pomembna območja za seleče se ujede v Vzhodnih Alpah], 73-75. Schneider-Jacoby, M.: A milestone on the Road to Natura 2000 [Mejnik na poti k Naturi 2000], 175179. Vrezec, A.: Slovenska ornitologija - včeraj, danes in jutri [Slovenian Ornithology - its Past, Present and Future], 1-5. Originalni članki / Original articles Avukatov, V. ^ Velevski, M., 181-282. Bengil, F., Uzilday, B. & Siki, M.: The distribution of breeding birds in the Kü^ük Menderes Delta in western Turkey [Razširjenost gnezdilk v delti Kü^ük Menderes (zahodna Turčija)], 115-130. Bordjan, D. & Rozoničnik, A.: Gnezditvena gostota velikega skovika Otus scops v naseljih otoka Brača (srednja Dalmacija) [Breeding density of the Scops Owl Otus scops in urban settlements on the island of Brač (Central Dalmatia)], 15-20. Božič, L. & Denac, D.: Številčnost in razširjenost izbranih gnezdilk struge reke Drave med Mariborom in Središčem ob Dravi (SV Slovenija) v letih 2006 in 2009 ter vzroki za zmanjšanje njihovih populacij [Abundance and distribution of selected breeding river-bed birds on the Drava River between Maribor and Središče ob Dravi (NE Slovenia) in 2006 and 2009, and causes of the reduction of their populations], 27-45. Božič, L. ^ Velevski, M., 181-282. Denac, D.: Population dynamics of the White Stork Ciconia ciconia in Slovenia between 1999 and 2010 [Populacijska dinamika bele štorklje Ciconia ciconia v Sloveniji med letoma 1999 in 2010], 101-114. Denac, D. ^ Božič, L., 27-45. Denac, K.: Census of migrating raptors at Breginjski Stol (NW Slovenia) - the first confirmed bottleneck site in Slovenia [Popis selečih se ujed na Breginjskem Stolu (SZ Slovenija) - prvo potrjeno ozko grlo v Sloveniji], 77-92. Grubač, B. ^ Velevski, M., 181-282. Hallmann, B. ^ Velevski, M., 181-282. Lisičanec, E. ^ Velevski, M., 181-282. Lisičanec, T. ^ Velevski, M., 181-282. Mero, T.O.: Breeding birds of shelterbelts near Sombor (NW Serbia) [Gnezdilke drevoredov pri Somboru (SZ Srbija)], 7-13. Mero, T.O., Žuljevič, A. & Varga, K.: Nest-site characteristics and breeding density of Magpie Pica pica in Sombor (NW Serbia) [Značilnosti gnezdišč in gnezditvena gostota srake Pica pica v Somboru (SZ Srbija)], 93-99. Rozoničnik, A. ^ Bordjan, D., 15-20. Siki, M. ^ Bengil, F., 115-130. Stoynov, E. ^ Velevski, M., 181-282. Štumberger, B. ^ Velevski, M., 181-282. Uzilday, B. ^ Bengil, F., 115-130. Varga, K. ^ mero, T.O., 93-99. Velevski, M., Hallmann, B., Grubač, B., Lisičanec, T., Stoynov, E., Lisičanec, E., Avukatov, V., Božič, L. & štumberger, B.: Important Bird Areas in Macedonia: Sites of global and European importance [Mednarodno pomembna območja za ptice globalnega in evropskega pomena v Makedoniji], 181-282. Vizi, A. & Vizi, O.: Changes in the diet composition of Pygmy Cormorant Phalacrocorax pygmeus on Skadar lake (Southern Montenegro) [Spremembe v prehrani pritlikavega kormorana Phalacrocorax pygmeus na Skadrskem jezeru (južna Črna gora)], 21—26. Vizi, O. ^ Vizi, A., 21—26. ŽuLjEvic, A. ^ Mero, T.O., 93—99. Kratki prispevki / Short Communications Bordjan, D.: Prvo opazovanje rdečevrate gosi Branta ruficollis v Sloveniji [First observation of the Red-breasted Goose Branta ruficollis in Slovenia], 53—55. Božič, L.: Rezultati januarskega štetja vodnih ptic leta 2010 v Sloveniji [Results of the International Waterbird Census (IWC) in January 2010 in Slovenia], 131—141. Chobanov, D. ^ Milchev, B., 143—145. Gašic, B.: First breeding record of the Syrian Woodpecker Dendrocopos syriacus in Bosnia and Herzegovina with a reference to its present status [Prvi podatek o gnezdenju in sedanji status sirijskega detla Dendrocopos syriacus v Bosni in Hercegovini], 47—51. Krofel, M.: Opažanja velikih jat krokarjev Corvus corax na Pokojiški planoti (osrednja Slovenija) [Observations of large Raven Corvus corax flocks on Pokojišče Plateau (Central Slovenia)], 147—149. Milchev, B., Chobanov, D. & Tzankov, N.: The Diet of a Lesser Spotted Eagle Aquilapomarina family in SE Bulgaria [Prehrana družine malega klinkača Aquila pomarina v JV Bolgariji], 143—145. Stumberger, B. ^ Velevski, M., 283—291. Tzankov, N. ^ Milchev, B., 143—145. Velevski, M. & Stumberger, B.: Review of the references on birds of Macedonia [Pregled virov o pticah Makedonije], 283—291. Iz ornitološke beležnice / From the ornithological notebook Basle, T. ^ Ploj, A., 64. Berce, T.: Rjavi jastreb Aegypius monachus, 59. Bombek, D.: Mala tukalica Porzana parva, 156—157, Duplar Columba oenas, 158, Hribski škrjanec Lullula arborea, 159—160. Bordjan, D.: Rdečegrli slapnik Gavia stellata, 57, Južni sokol Falco biarmicus, 60—61, Čopasti ponirek Podiceps cristatus, 151, Kanja Buteo buteo, 154—155, Planinski orel Aquila chrysaetos, 156, Rdečenoga postovka Falco vespertinus, 156, Mala uharica Asio otus, 158—159, Močvirska uharica Asio flammeus, 159, Rjava cipa Anthus campestris, 160, Rdečegrla cipa Anthus cervinus, 160, Citronasta pastirirca Motacilla citreola, 161, Taščična penica Sylvia cantillans, 162, Dolgorepka Aegithalos caudatos, 163, Rjavi srakoper Lanius collurio, 163, Šoja Garrulus glandarius, 163— 164. Bračko, F.: Pegam Bombycilla garrulus, 161—162, Severni kovaček Phylloscopus trochilus, 162. CiGLič, H.: Polojnik Himantopus himantopus, 61—62. Denac, D.: Veliki prodnik Calidris canutus & ozkokljuni liskonožec Phalaropus lobatus, 62, Kozica Gallinago gallinago, 62—63. Denac, K.: Črnoglavi strnad Emberiza melanocephala, 164—165. Fekonja, D.: Snežni strnad Plectrophenax nivalis, 65, Plotni strnad Emberiza cirlus, 66. Gamser, M.: Rjavi lunj Circus aeruginosus, 153, Stepski lunj Circus macrourus, 154, Mali škurh Numenius phaeopus, 158, Planinski hudournik Apus melba, 159. Gamser, M. ^ ploj, A., 67, 68, 165. Hanžel, J.: Cattle Egret Bubulcus ibis, 68, Citronasta pastirirca Motacilla citreola, 160—161. Jovicevic, M.: Golden Eagle Aquila chrysaetos, 167— 168. Jovicevic, M. & ŠiMic, E.: Flamingo Phoenicopterus roseus, 167. Jovicevic, M. ^ Rubinic, B., 168—169, 169. Koren, A.: Rožnati pelikan Pelecanus onocrotalus, 57, Kanadska gos Branta canadensis, 58, Čopasta čaplja Ardeola ralloides, 151. Kozina, A.: Dular Charadrius morinellus, 62. Krečič, P.: Stepski lunj Circus macrourus, 60. Lanszki, J. ^ Purger, J.J., 66. Mozetič, B.: Kravja čaplja Bubulcus ibis, 151—152, Mala gos Anser erythropus in rdečevrata gos Branta ruficollis, 152—153, Mala droplja Tetrax tetrax, 157. Ploj, A. & Basle, T.: Kratkoprsti škrjanček Calandrella brachydactyla, 64, Rjava cipa Anthus campestris, 64. Ploj, A. & Gamser, M.: Laški Škrjanec Melanocorypha calandra, 67, Rdečegrla cipa Anthus cervinus, 68, Rdeča lastovka Cecropis daurica, 165. Purger, J.J.: Caspian Tern Hydroprogne caspia, 66—67, Tawny Owl Strix aluco, 67. Purger, J.J. & Lanszki, J.: Squacco Heron Ardeola ralloides, 66. Rubinic, B. & Jovicevic, M.: Great Snipe Gallinago media, 168—169, Short-eared Owl Asio flammeus, 169. Sackl, P. & Štumberger, B.: Whiskered Tern Chlidonias hybrida, 169. Saveljic, D.: Golden Eagle Aquila chrysaetos, 168, Great Bustard Otis tarda, 168. Saveljic, D. ^ Velevski, M., 69—70. Šalamun, Ž.: Stepski lunj Circus macrourus, 153—154, Rjasta kanja Buteo rufinus, 155. Šciban, M.: Black-throated Diver Gavia arctica, 68, Pallid Harrier Circus macrourus, 68, Crane Grus grus, 69. Šimic, E. ^ Jovicevic, M., 167. Šere, D.: Grmovščica Phylloscopussibilatrix, 65, Puklež Lymnocryptes minimus, 157—158, Ribji orel Pandion haliaetus, 165, Rdečegrla cipa Anthus cervinus, 165— 166, Citronasta pastirica Motacila citreola, 166—167. Šinigoj, E.: Zlatovranka Coraciasgarrulus, 63—64. Škoberne, A.: Plevica Plegadis falcinellus, 57, Kostanjevka Aythya nyroca, 58—59. Škoberne, A. & Božič, L.: Kričava čigra Sterna sandvicensis, 63. Štumberger, B. ^ Sackl, P., 169. Trocsanyi, B.: Little Tern Sternula albifrons, 67. Velevski, M.: Crane Grus grus, 69. Velevski, M. & Saveljic, D.: Great Black-headed Gull Larus ichthyaetus, 69—70. Vidmar, J.: Žerjav Grus grus, 61. VreŠ, I.: Mušja listnica Phylloscopus inornatus, 64—65, Mali strnad Emberizapusilla, 66. Vrezec, A. & Vrh Vrezec, P.: Žličarka Platalea leucorodia, 57—58, Duplar Columba oenas, 63. Vrh Vrezec, P. ^ Vrezec, A., 57—58, 63. Najave in obvestila / Announcements Koce, U.: Nagrada zlati legat 2008-2009 [The Golden Bee-eater Award 2008-2009], 173—174. Kazalo znanstvenih imen ptic / Index of scientific names of birds A Accipiter brevipes 181 Accipiter gentilis 77 Accipiter nisus 77 Acrocephalus arundinaceus 115 Acrocephalus scirpaceus 115, 181 Acrocephalus paludicola 181 Acrocephalus palustris 156, 181 Acrocephalus schoenobaenus 181 Actitis hypoleucos 27, 115, 131, 181 Aegithalos caudatos 163 Aegypius monachus 59, 181 Aix galericulata 131 Alauda arvensis 159, 181 Akedo atthis 27, 61, 131, 181 Alectoris graeca 181 Anas acuta 131, 181 Anas clypeata 131, 181 Anas crecca 131, 181 Anas penelope 131, 181 Anasplatyrhynchos 61, 115, 131, 181 Anas querquedula 181 Anas strepera 131, 181 Anser albifrons 131, 152 Anser anser 53, 58, 131 Anser erythropus 152, 181 Anser fabalis 131 Anthus campestris 64, 160, 181 Anthus cervinus 68, 160, 165 Anthus pratensis 165 Apus pallidus 181 Aquila chrysaetos 77, 156, 167, 168, 181 Aquila clanga 181 Aquila heliaca 181 Aquila nipalensis 181 Aquila pennata 77, 181 Aquila pomarina 143, 181 Ardea cinerea 61, 66, 131, 156, 181 Ardea purpurea 181 Ardeola ralloides 21, 66, 151, 165, 181 Asio flammeus 159, 169 Asio otus 158, 173 Athene noctua 15, 115, 181 Aythya nyroca 58, 131, 174, 181 Aythya ferina 58, 131, 181 Aythya ferina x A. nyroca 131 Aythya fuligula 58, 131, 181 Aythya marila 131 B Bombycilla garrulus 161 Botaurus stellaris 131, 181 Branta ruficollis 53, 152, 181 Branta canadensis 58, 131 Bubo bubo 181 Bubulcus ibis 68, 151 Bucephala clangula 58, 131, 181 Burhinus oedicnemus 1, 181 Buteo buteo 77, 115, 154, 155, 156, 167 Buteo rufinus 155, 181 C Cairina moschata 131 Calandrella brachydactyla 64, 181 Calidris alpina 131 Calidris canutus 62 Calidris minuta 131 Caprimulgus europaeus 181 Carduelis cannabina 159, 181 Carduelis carduelis 7, 115 Carduelis chloris 7, 115, 181 Carduelis spinus 159, 181 Casmerodius albus 61, 131, 181 Cecropis daurica 165 Cercotrichas galactotes 181 Certhia brachydactyla 181 Cettia cetti 115 Charadrius alexandrinus 115 Charadrius dubius 27, 115 Charadrius morinellus 62 Chlidonias hybrida 169, 181 Chlidonias leucopterus 115 Chlidonias niger 115, 181 Chroicocephalus ridibundus 60, 131, 181 Ciconia ciconia 101, 115, 131, 153, 181 Ciconia nigra 143, 181 Cinclus cinclus 131 Circaetus gallicus 77, 181 Circus aeruginosus 60, 77, 131, 153, 154, 155 Circus cyaneus 60, 68, 77, 153 Circus macrourus 60, 68, 153, 154, 181 Circuspygargus 60, 68, 77, 153, 154, 181 Cisticola juncidis 115 Clamator glandarius 115 Coccothraustes coccothraustes 7 Columba livia domestica 63 Columba oenas 63, 158, 181 Columba palumbus 153, 181 Coraciasgarrulus 63, 115, 181 Corvus corax 147, 167, 168, 173 Corvus cornix 7, 93, 115 Corvus monedula 115, 181 Coturnix coturnix 181 Crex crex 181 Cuculus canorus 7, 115 Cygnus cygnus 131 Cygnus olor 53, 131, 181 D Delichon urbicum 115, 181 Dendrocopos major 47 Dendrocopos medius 181 Dendrocopos syriacus 7, 47, 115, 181 Dendrocopos syriacus x D. major 47 E Egretta garzetta 21, 131, 181 Emberiza cia 181 Emberiza cirlus 66, 115, 181 Emberiza citrinella 181 Emberiza hortulana 181 Emberiza melanocephala 115, 164, 181 Emberizapusilla 66 Eremophila alpestris 181 Erithacus rubecula 181 F Falco biarmicus 60, 181 Falco cherrug 60, 181 Falco eleonorae 60 Falco naumanni 1, 175, 181 Falcoperegrinus 60, 77, 153, 167, 181 Falco subbuteo 60, 77 Falco tinnunculus 7, 60, 77, 115, 167, 181 Falco vespertinus 63, 73, 77, 156, 181 Ficedula albicollis 181 Ficedula semitorquata 181 Fringilla coelebs 7, 143, 159, 181 Fringilla montifringilla 159 Fulica atra 68, 115, 131, 181 G Galerida cristata 115, 159, 181 Gallinula chloropus 115, 131, 154 Gallinago gallinago 61, 62, 131, 157, 168 Gallinago media 168, 181 Garrulus glandarius 115, 163 Gavia arctica 68, 131, 181 Gavia stellata 57, 131 Glareola pratincola 115 Grus grus 61, 69, 131 Gypaetus barbatus 181 Gyps fulvus 59, 77, 181 H Haliaeetus albicilla 131 Himantopus himantopus 61, 115 Hippolais olivetorum 181 Hippolais pallida 115, 181 Hirundo rustica 115, 165, 181 Hydrocoloeus minutus 131 Hydroprogne caspia 66 I Ixobrychus minutus 115, 174, 181 J Jynx torquilla 181 L Lanius collurio 7, 115, 163, 181 Lanius excubitor 158 Lanius minor 115, 181 Lanius nubicus 181 Lanius senator 115, 181 Larus argentatus 131 Larus cachinnans 131, 181 Larus canus 131 Larus ichthyaetus 69, 181 Larus melanocephalus 131 Larus michahellis 53, 66, 69, 115, 131, 153, 181 Limosa limosa 181 Locustella luscinioides 181 Lullula arborea 63, 159, 181 Luscinia megarhynchos 7, 181 Lymnocryptes minimus 157 M Marmaronetta angustirostris 181 Melanitta fusca 131 Melanitta nigra 131 Melanocorypha calandra 67, 115, 181 Mergellus albellus 131, 181 Mergus merganser 131, 181 Mergus serrator 131 Merops apiaster 181 Miliaria calandra 7, 115, 181 Milvus migrans 77, 181 Milvus milvus 77, 181 Monticola saxatilis 181 Monticola solitarius 181 Montifringilla nivalis 181 Motacilla alba 7 Motacilla citreola 160, 161, 166 Motacilla flava 68, 115, 160, 166 Muscicapa striata 7, 115, 181 N Neophron percnopterus 175, 181 Netta rufina 131, 181 Numenius arquata 131, 158, 181 Numenius phaeopus 158 Numenius tenuirostris 181 Nycticorax nycticorax 21, 181 O Oenanthe hispanica 181 Oenanthe oenanthe 181 Oriolus oriolus 7 Otis tarda 168, 181 Otus scops 15, 67, 173, 181 Oxyura leucocephala 181 P Pandion haliaetus 153, 165 Parus caeruleus 181 Parus cristatus 181 Parus lugubris 181 Parus major 7, 115 Parus palustris 181 Passer domesticus 115, 181 Passer hispaniolensis 115 Passer montanus 7, 181 Pelecanus crispus 115, 181 Pelecanus onocrotalus 57, 181 Perdix perdix 181 Pernis apivorus 73, 77, 153, 154, 181 Phalacrocorax aristotelis 66, 131 Phalacrocorax carbo 21, 53, 131, 181 Phalacrocorax pygmeus 21, 63, 115, 131, 181 Phalaropus lobatus 62 Phoenicopterus roseus 167 Phoenicurus phoenicurus 181 Phylloscopus bonelli 181 Phylloscopus inornatus 64 Phylloscopus sibilatrix 65 Phylloscopus trochilus 162 Pica pica 7, 93, 115 Picus canus 181 Picus viridis 7, 181 Platalea leucorodia 57 Plectrophenax nivalis 65 Plegadis falcinellus 21, 57 Pluvialis squatarola 131 Podiceps auritus 131 Podiceps cristatus 68, 131, 151, 181 Podiceps nigricollis 131, 181 Porzana parva 156 Porzana porzana 174 Prunella collaris 181 Prunella modularis 181 Pyrrhocorax graculus 181 Pyrrhocorax pyrrhocorax 181 R Rallus aquaticus 61, 131, 156 Remiz pendulinus 115 Regulus ignicapilla 181 Regulus regulus 181 Riparia riparia 181 S Saxicola torquatus 115 Saxicola rubetra 181 Scolopax rusticola 131, 181 Serinus serinus 181 Sitta neumayer 181 Sterna hirundo 181 Sterna sandvicensis 63, 131 Sternula albifrons 67, 181 Streptopelia decaocto 7, 115 Streptopelia turtur 115, 181 Strix aluco 67, 181 Sturnus roseus 143 Sturnus vulgaris 7, 181 Sylvia atricapilla 7,181 Sylvia borin 181 Sylvia cantillans 162, 181 Sylvia communis 7, 181 Sylvia hortensis 181 Sylvia melanocephala 181 Sylvia nisoria 181 T Tachybaptus ruficollis 131, 158, 181 Tadorna ferruginea 115 Tadorna tadorna 131 Tetrao urogallus 173, 181 Tetrax tetrax 157, 181 Tichodroma muraria 181 Tringa erythropus 131 Tringa glareola 166 Tringa nebularia 131 Tringa ochropus 131 Tringa totanus 62, 115, 131 Turdus merula 7, 115, 181 Turdus philomelos 181 Turdus torquatus 181 Turdus viscivorus 181 Tyto alba 143, 181 U Upupa epops 115, 181 V Vanellus spinosus 115 Vanellus vanellus 131, 152, 181 Seznam recenzentov letnika 31 (2010) The list of manuscript reviewers of Volume 31 (2010) Spisek recenzentov, ki so pregledovali prispevke v reviji Acrocephalus za letnik 31, 2010. Njihov delež pri nastajanju revije je bil velik in ključen pri objavljanju kvalitetnih prispevkov. Urednik se zato vsem iskreno zahvaljuje za opravljene recenzije v minulem letu. Imena recenzentov so urejena po abecednem vrstnem redu brez akademskih naslovov, a z oznakami držav: The list of manuscript reviewers for the journal Acrocephalus in Volume 31, 2010. Their contribution was great and essential in preparing high quality papers published in Volume 31. The Editor would like to thank them for their work in the past year. Names of reviewers are presented in alphabetical order without academic titles but with abbreviations of their countries: Dejan Bordjan (SI) Luka Božič (SI) Ian Burfield (GB) Alain J. Crivelli (FR) Katarina Denac (SI) Janez Gregori (SI) Tomaž Hojnik (SI) Max Kasparek (DE) Guy M. Kirwan (GB) Ursa Koce (SI) Dražen Kotrosan (BA) Krzysztof Kujawa (PL) Gordan Lukač (HR) Boris Nikolov (BG) Remo Probst (AT) Jenö J. Purger (HU) Slobodan Puzovic (RS) Andreja Radovic (HR) Borut Rubinic (SI) Peter Sackl (AT) Reto Spaar (CH) Borut Štumberger (SI) Davorin Tome (SI) Tomi Trilar (SI) Marko Tucakov (RS) Piotr Tryjanowski (PL) Najboljše družabno omrežje Pred dvajsetimi leti je zapihal svež veter. In pod skoraj vsak kamen, tudi v najbolj odmaknjene konce Slovenije, ponesel Mobitelov signal. Za vedno je spremenil komunikacijo in ljudi še tesneje povezal med seboj. Svet kar naenkrat nosite v žepu, prijatelje pa imate vedno s seboj v imeniku mobitela. In vsakič, ko vam zazvoni mobitel, veste, da ste del najboljšega družabnega omrežja. 2G" WWW.MOBITEL.SI Navodila za avtorje / Instructions for authors Original work on all fields of ornithology, without any geographical limitation, is published in Acrocephalus. However, articles covering the south-eastern European and eastern Mediterranean regions are particularly encouraged. The contributions should not have been submitted for publication elsewhere. 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(1997): Penduline Tit Remiz pendulinus. pp. 656-657 In: Hagemaijer, W.J.M. & Blair, M.J. (eds.): The EBCC Atlas of European Breeding Birds. - T & AD Poyser, London. Cited as: DiEDRiCH et al. (1997). short note: Bordjan, D. (2005): Sombre Tit Parus lugubris. -Acrocephalus 26 (125/126): 147-157. Cited as: Bordjan (2005). theses: Kuhar, B. (2005): [Diet of the Tawny Owl Strix aluco in Kozjansko Regional Park]. - BSc thesis, University of Maribor. (in Slovene) Cited as Kuhar (2005). internet sources: BirdLife International (2004): Species factsheet: Pygmy Cormorant Phalacrocorax pygmeus. - [www.birdlife.org], 10/5/2010. Cited as BirdLife International (2004). legislation: Uradni list RS (2004): Uredba o ekološko pomembnih območjih (no. 48/04). Cited as Uradni list RS (2004). When quoting congress proceedings quote proceedings title, the organization and town. 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Please check the journal's home page [www. ptice.org] for further instructions and the Slovene text. Vsebina / Contents letnik 31 volume 31 številka 147 number 147 strani 175-301 pages 175-301 Uvodnik / Editorial C/3 Ph PM 175 A Milestone on the Road to Natura 2000 (M. Schneider-Jacoby) Mejnik na poti k Naturi 2000 (M. Schneider-Jacoby) Originalni članki / Original articles l8l Important Bird Areas in Macedonia: Sites of Global and European Importance (m. Velevski, B. Hallmann, B. Grubač, T. Lisičanec, E. Stoynov, E. Lisičanec, V. Avukatov, L. Božič 8c B. Štumberger) Mednarodno pomembna območja za ptice globalnega in evropskega pomena v Makedoniji (m. Velevski, B. Hallmann, B. Grubač, T. Lisičanec, E. Stoynov, E. Lisičanec, V. Avukatov, L. Božič & B. Štumberger) Kratki prispevki / Short communications 283 Review of the references on birds of Macedonia (m. Velevski & B. Štumberger) Pregled virov o pticah Makedonije (M. Velevski & B. Štumberger) 293 Kazalo letnika 31 (2010) / Index ofVolume 31 (2010) 3OI Seznam recenzentov / The list of manuscript reviewers Sponzor DOPPS ŽIVLJENJE NISO LE BESEDE WWW.MOBITEL.SI